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Deconstruction in the Lifecycle of Constructions Manuel Guilherme Palma Leal Ceppas Catarino Thesis to obtain the Master of Science Degree in Civil Engineering Supervisors: Professor Doctor Fernando António Baptista Branco and Coordinator Investigator Armando Narciso da Costa Manso Examination Committee Chairperson: Professor Doctor Ana Paula Patrício Teixeira Ferreira Pinto França de Santana Supervisor: Coordinator Investigator Armando Narciso da Costa Manso Members of the Committee: Professor Doctor Manuel Guilherme Caras Altas Duarte Pinheiro October 2014
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Page 1: Deconstruction in the Lifecycle of Constructions · PDF fileDeconstruction in the Lifecycle of Constructions Manuel Guilherme Palma Leal Ceppas Catarino Thesis to obtain the Master

Deconstruction in the Lifecycle of Constructions

Manuel Guilherme Palma Leal Ceppas Catarino

Thesis to obtain the Master of Science Degree in

Civil Engineering

Supervisors: Professor Doctor Fernando António Baptista Branco

and Coordinator Investigator Armando Narciso da Costa Manso

Examination Committee

Chairperson: Professor Doctor Ana Paula Patrício Teixeira Ferreira Pinto França de

Santana

Supervisor: Coordinator Investigator Armando Narciso da Costa Manso

Members of the Committee: Professor Doctor Manuel Guilherme Caras Altas Duarte

Pinheiro

October 2014

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Acknowledgments

Foremost, I would like to express my sincere gratitude and appreciation towards my dissertation

supervisors, Prof. Fernando Branco and Eng. Armando Manso, who have been extremely supportive

during the course of this research project. I would like to thank them for his guidance, encouragement

and enthusiasm throughout the duration of the project. I am also extremely grateful for the help given

by Eng. António Cabaço from LNEC, whose contribution was decisive in defining the course of this

thesis.

I would like to thank the support provided by my family, in particular my parents and sisters, who

have supported me throughout my academic life, as well as my godfather who was always available to

give me advice. They have stood behind the decisions I have made, being a never ending source of

inspiration, strength and dedication.

I would also like to extend my gratitude towards my close friends Hugo Borges, and Mafalda

Ceyrat for the help provided through informal discussions which led me to gain new ideas and

motivation to bring this thesis to fruition.

Finally, I am grateful to my University – Instituto Superior Técnico - for giving me the challenge

and opportunity to explore my academic interests and present it in the form of this thesis.

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Resumo

A demolição de construções é um processo gerador de resíduos. No caso de as construções

terem o fim-de-vida determinado pelo fim da sua funcionalidade física ou económica uma grande

quantidade dos seus resíduos pode ser provavelmente valorizada, prevenindo a necessidade da sua

eliminação. A Desconstrução permite remover materiais e elementos de construção da obra

mantendo a sua integridade com o objetivo de mais tarde os reintegrar noutra construção.

Os objetivos de estudo são de compreender os motivos que levaram ao excessivo consumo de

recursos e produção de resíduos na construção; de aprender quais os hábitos e técnicas de

desconstrução que estão atualmente em prática por entidades ligadas ao sector; de identificar os

aspetos que poderiam melhorar a prática de desconstrução por parte de empresas sem acrescentar

complexidade ao modo de funcionamento das mesmas; de reduzir de forma indireta a produção de

RCD (resíduos de construção e demolição) e o consumo de matéria-prima, proporcionando uma

compreensão mais profunda sobre o conceito de desconstruir e sugerindo a sua utilização em futuras

obras; de procurar uma solução inovadora em tecnologias de informação que contribua para reduzir o

fim de vida prematuro de elementos construtivos.

Os dois grandes obstáculos que a Desconstrução enfrenta são a inexistência de legislação que

promova a sua prática de forma independente da reciclagem, e o risco envolvido em não encontrar

um destino para os materiais que foram desconstruídos e que representaram um acréscimo de custos

de demolição numa outra obra.

Palavras-chave: Desconstrução, Gestão de RCD; Sustentabilidade; Avaliação de Ciclo de Vida;

Gestão de Demolições.

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Abstract

A significant amount of waste is generated by the demolition of constructions. Some of the waste

generated by buildings that have had their end of life determined by the end of their functionality may

probably still have value, and its disposal might be prevented. Deconstruction is the process of

removing the waste in the form of construction materials or elements maintaining its integrity in order

to reintegrate in another construction work.

The objectives of this study are to understand the reasons that lead to the excessive consume of

resources and high levels of waste production in construction; to learn what deconstruction habits and

techniques are currently applied by entities linked to the construction sector; to identify aspects in

which deconstruction could be better practiced without adding significant complexity in the mode of

operation of a deconstruction related company; to indirectly reduce the production of construction

waste and the consumption of virgin raw material by giving a deeper understanding of the concept and

process of deconstructing and suggesting it as a solution for forthcoming construction or demolition

works; and to seek a unique information technology solution that can contribute to reducing the

premature end of life of building elements and materials.

The two main obstacles that Deconstruction is facing are the lack of legislation promoting its

practice separately from recycling, and the risk involved in not finding a suitable receiver for the

deconstructed materials that brought up the costs of demolition.

Keywords: Deconstruction, C&DW Management; Sustainability; Lifecycle Assessment; Demolition

Planning.

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Contents

Deconstruction in the Lifecycle of Constructions ...............................................................................i

Acknowledgments ..............................................................................................................................i

Resumo ............................................................................................................................................. ii

Abstract ............................................................................................................................................ iii

Contents ........................................................................................................................................... iv

Definitions ........................................................................................................................................ vii

Acronyms and Abbreviations.......................................................................................................... viii

List of Tables .................................................................................................................................... ix

List of Figures ....................................................................................................................................x

1. Introduction .............................................................................................................................. 1

1.1. Overview .......................................................................................................................... 1

1.2. Scope ............................................................................................................................... 1

1.3. Aims ................................................................................................................................. 2

1.4. Methodology .................................................................................................................... 3

1.5. Structure .......................................................................................................................... 3

1.6. Previous notes ................................................................................................................. 4

2. Sustainability in Construction .................................................................................................. 5

2.1. Initial considerations ........................................................................................................ 5

2.2. Definition and characterization of C&DW ........................................................................ 7

2.3. Potential environmental impact of C&DW ..................................................................... 10

2.4. Legal framework on C&DW ........................................................................................... 11

2.4.1. Legal framework in Europe ........................................................................................ 11

2.4.2. Legal framework in Portugal ...................................................................................... 12

2.5. Milestones for Sustainability .......................................................................................... 16

2.6. Hierarchy of waste management in Construction .......................................................... 17

2.7. Eco-efficiency ................................................................................................................ 19

2.8. Embodied energy concept ............................................................................................. 19

2.9. Lifecycle Assessment .................................................................................................... 21

2.10. Green Building Certification ........................................................................................... 23

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2.10.1. BREEAM ................................................................................................................ 24

2.10.2. LEED ..................................................................................................................... 24

2.10.3. HQE ....................................................................................................................... 26

2.11. Chapter remarks ............................................................................................................ 27

3. Deconstruction in the Lifecycle of Constructions................................................................... 28

3.1. Initial considerations ...................................................................................................... 28

3.2. Application of the term Deconstruction .......................................................................... 28

3.3. History of Deconstruction .............................................................................................. 29

3.4. International overview of Deconstruction practices ....................................................... 31

3.5. Recent Deconstruction .................................................................................................. 32

3.5.1. Deconstructions on the source .................................................................................. 33

3.5.2. Deconstructions from source to destination .............................................................. 34

3.5.3. Deconstruction of temporary elements ...................................................................... 35

3.5.4. Dislocation deconstructions ....................................................................................... 37

5.1.1. Constructions that include deconstructed materials .................................................. 40

5.2. Principles for an optimized deconstruction process ...................................................... 43

5.3. Variables when choosing Deconstruction ..................................................................... 44

5.3.1. Choosing Deconstruction on constructions ............................................................... 44

5.3.2. Choosing Deconstruction on demolitions .................................................................. 45

5.4. Design for Deconstruction ............................................................................................. 46

5.5. Deconstruction equipment ............................................................................................. 49

5.6. Legislation that supports Deconstruction ...................................................................... 51

5.7. Chapter remarks ............................................................................................................ 52

5.7.1. SWOT analysis .......................................................................................................... 53

4. Deconstruction Supporting Platform ...................................................................................... 55

4.1. Initial considerations ...................................................................................................... 55

4.2. Aims ............................................................................................................................... 56

4.3. Analysis of the current deconstructed materials market................................................ 56

4.4. Target ............................................................................................................................ 57

4.5. Concept of the platform ................................................................................................. 57

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4.6. Login, registration and verification of the entities .......................................................... 58

4.7. Security .......................................................................................................................... 59

4.8. Publishing on the platform ............................................................................................. 59

4.9. The database ................................................................................................................. 62

4.10. Revenues and costs ...................................................................................................... 64

4.11. Chapter remarks ............................................................................................................ 64

5. Future Developments and Conclusions ................................................................................ 65

5.1. Future Developments .................................................................................................... 65

5.2. Conclusions ................................................................................................................... 66

References ..................................................................................................................................... 67

Appendixes ........................................................................................................................................ I

A - Prices charged for incoming materials at TRIANOVO recycling plant .................................. II

B - Sector 17 of the European List of Wastes, regarding C&DW.. ............................................ III

C - Lifecycle Assessment Software and Databases ................................................................... V

D - Average embodied energy in construction materials ........................................................... VI

E - Savaged materials from the Vancouver Materials Testing Lab ........................................... VII

F - Detailed cost report for TriPOD’s Shell and Structure ........................................................ VIII

G - Detailed cost report for TriPOD’s Systems .......................................................................... IX

H - Detailed cost report for TriPOD’s finish materials ................................................................. X

I - Mass, embodied energy, and specific embodied energy of the materials that

composed the Macau Pavilion at Expo 98 ............................................................................ XI

J - Template of the email that was sent to 72 different portuguese construction

industry and deconstruction related companies. ................................................................. XII

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Definitions

Construction materials

Material, or supply consumed or used in a construction project and incorporated in the constructed building.

Construction elements

Aggregation of construction materials, that when grouped together form the construction.

Construction waste

recycling

Separation and recycling of recoverable waste materials generated during construction and remodeling.

Upcycling Process of converting waste materials or useless products into new materials or products of better quality or for better environmental value.

Downcycling Process of converting waste materials or useless products into new materials or products of lesser quality and reduced functionality.

Bioclimatic design

Design of buildings and spaces based on local climate with the intent of providing thermal and visual comfort and making use of solar energy and other environmental sources.

Refurbishing Service of renovating or reconditioning of older or damaged materials to bring

them to a workable or better looking condition.

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Acronyms and Abbreviations

C&DW

Construction and Demolition Waste

LCA

Lifecycle Assessment

MSW

Municipal Solid Waste

DfD

Design for Deconstruction

BREEAM

Building Research Establishment Environmental Assessment Method

EU

European Union

EC

European Commission

CIB

Conseil International du Bâtiment

USA

United States of America

SB Tool

Green Building Tool

ISO

International Standard Organization

LEED

Leadership in Energy and Environmental Design

LNEC

Laboratório Nacional de Engenharia Civil

OCDE

Organization for Economic Co-operation and Development

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List of Tables

Table 1 - Composition of C&DW as percentage by weight ..................................................................... 8

Table 2 - Hazardous C&DW in the European List of Wastes ................................................................ 10

Table 3 - Average embodied energy in construction materials ............................................................. 20

Table 4 -Energy consumption in transport ............................................................................................ 20

Table 5 - Lifecycle Assessment Software and Databases .................................................................... 22

Table 6 - Green building certification systems, their origin and the entities who promoted their

creation. ................................................................................................................................ 23

Table 7 - Costs and revenues for demolishing and dismantling options of the unfinished office

buildings ................................................................................................................................ 33

Table 8 - Maximum distance worth moving for a reclaimed material before the environmental

advantage is lost ................................................................................................................... 44

Table 9 - Used construction materials companies ................................................................................ 57

Table 10 - Example of the Deconstruction platform’s raw database after the publication of eleven

material/element forms.......................................................................................................... 63

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List of Figures

Figure 1 - Current and estimated population resource consumption in comparison to the world's

resource regeneration ........................................................................................................... 6

Figure 2 - Current resource consumption in Portugal ............................................................................. 7

Figure 3 - Logo of the Organized Waste Market ................................................................................... 15

Figure 4 - Waste Management Hierarchy for demolition and construction operations ......................... 18

Figure 5 - Lifecycle of construction materials ........................................................................................ 22

Figure 6 - Six general areas of the LEED NC category, and their given weight ................................... 25

Figure 7 - Roman Colosseum's punctured pilars and walls. The holes were part of a original marble

coating support mechanism. ............................................................................................... 30

Figure 8 - Constitutive elements of roman pillars used as foundations in Notre Dame's Cathedral ..... 30

Figure 9 - Unfinished office buildings .................................................................................................... 33

Figure 10 - Composition of pictures from the decommission and deconstruction of a barracks

building in Fort Ord.............................................................................................................. 34

Figure 11 - Construction timeline for the Vancouver Materials Testing Lab. ........................................ 35

Figure 12 - "Mallforms" temporary walls for offices and temporary barricades for shopping centers ... 36

Figure 13 - "ENVY Modular Wall Systems” creating a temporary partition and its patented award

winning hinge schematics ................................................................................................... 36

Figure 14 - The Pavilion of Macau in use during Expo 98 and it’s deconstruction process .................. 37

Figure 15 - Rebuilding of the Pavilion of Macau.................................................................................... 37

Figure 16 - Kaisersaal in Berlin’s Sony Center, before translocation .................................................... 38

Figure 17 - Scheme for the translocation of Kaisersaal, Berlin ............................................................. 39

Figure 18 - Translocation of Kaisersaal, Berlin ..................................................................................... 39

Figure 19 - Deconstructed railway sleepers used as structural elements for a balcony in a private

house in Beirã viewed from above and below. ................................................................... 40

Figure 20 - Don Justo’s Cathedral ......................................................................................................... 41

Figure 21 - Infinisky’s constructions: on the left the El Tiemblo house and on the right the Manifesto

house .................................................................................................................................. 41

Figure 22 - Slum in the city of Ho Chi Minh, Vietnam ........................................................................... 42

Figure 23 - TriPOD Plug and Play Housing System ............................................................................. 48

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Figure 24 - Mobile Lead Based Paint Removal System ........................................................................ 50

Figure 25 - Nail Kicker tool .................................................................................................................... 50

Figure 26 - Links between the entities involved in Deconstruction ....................................................... 58

Figure 27 - Diagram of the connections between the Decontruction supporting platform's clients and

the platform itself ................................................................................................................. 59

Figure 28 - Construction material/element publishing form ................................................................... 61

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1. Introduction

1.1. Overview

All over the world mankind is evolving. Tradition links us to our past, without it we would lose our

identity. But some traditions can’t be kept. They come from a time where humanity didn’t have to worry

about the problems of today, and to be unable to abandon these traditions may be our sentence.

Ravaging economic growth isn’t anymore the key to evolution, but to grow in a sustainable way,

investing in the future generations and having into consideration the legacy that will be left for them.

The moment of change is known to be most likely to happen while facing the blade of the sword.

Humanity has had its share of warnings, and Earth can’t sustain its burden forever. In the same way

that in a student’s life there is a moment when he completes his degree and starts a self-sustainable

living, humanity too must learn to stop depending on an allowance.

Sustainability is now an objective, and a rather complex one to accomplish. There isn’t a sole road

to achieving sustainability, but hundreds of trails instead, and deconstruction is one of these trails. So

far it’s still a small one, but it has the potential to be traveled by everyone.

1.2. Scope

The motivation to research Deconstruction emerged during the production of a scholar group work

for the course Construction Technology in Engineering Works, coordinated by the supervisor of this

thesis. Throughout discussions with colleagues grew the perception that Deconstruction is

understudied, underdeveloped but should not be underrated. Deconstruction lacked solid studies and

was not yet fully adapted to the new technologies, especially information technology. This also led to

the discovery of a “niche” on the lack of information technology in the used construction materials

market. The author and both supervisors decided to rise up to the challenge and moved forward into

doing a study on the Deconstruction in the Lifecycle of Buildings.

No construction work is eternal, when a building reaches a certain stage of its life it has to face

obsolescence. In the same way that the bearing capacity of a chain corresponds to the capacity of its

weakest link, the life of a building also corresponds to the durability of its first element to have reached

its lifecycle end (Lobato dos Santos, 2010). This can happen due many different reasons, such as

inadaptability to new technologies, unintegrated architectural design, end of motive for existence, or

even the need for an amount of repairs so expensive that it’s deemed not worth prolonging its

existence. Depending on the circumstance, there is a choice to be made in which approach should be

taken for the obsolete construction. The choice dwells between repairing, demolishing or abandoning

the construction.

The demolition of a building is traditionally a waste generating process. The generated waste can

be taken care of with different levels of concern. A conventional demolition seeks only to remove the

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construction materials from the worksite, and with that sole intent, the easiest way to remove it is the

destruction of its elements without concern for the characteristics of each.

In the case of seeking a selective approach regarding the type of materials to demolish (selective

demolition) there is the possibility to separate waste by material composition, so that materials with

different characteristics can have different destinations, including recycling or deposit. But it can often

be found that not all elements of a construction in demolition phase have reached the end of their

useful life. Some may be in excellent condition, and destroying them would be a loss. Buildings that

have been subject of recent partial rehabilitation are an example of a good source of construction

elements that may have a significant amount of material whose lifetime is far from expiry.

The process of deconstruction is defined as the careful removal of these materials with the intent

to re-integrate them into a new construction or rehabilitation work. Through this process it’s possible to

give construction elements an effective service life again closer to its maximum service life, while

simultaneously reducing the production of demolition waste, the extraction of virgin raw materials and

reducing the energy costs that result from their transformation.

Deconstruction can also be viewed as a concept that includes not only the activity of

deconstruction, but also the industry of Deconstruction and its inherent activities like designing for

deconstruction, the refurbishment of deconstructed materials and deconstruction materials

management.

Deconstruction can take part along the lifecycle of a construction from its grave to its cradle.

Before its building process, a construction can be designed taking into account its future

deconstructability. During its construction phase and repairs a construction can incorporate used

constructed materials that originated from deconstruction processes, and in its lifecycle end a

construction can be dismantled into components/materials, henceforth as above cited, deconstructed.

1.3. Aims

This dissertation aims at five different targets:

The first is to study and understand the reasons that lead to the well-known issue of excessive

consume of resources and high levels of waste production in construction that mankind is facing;

With the study involved in making this thesis, the second aim is to seek to learn what

deconstruction habits and techniques are currently applied by entities linked to the construction sector;

In its learning journey the third aim points at identifying aspects in which deconstruction could be

better practiced without adding significant complexity in the mode of operation of an enterprise related

to Deconstruction;

A fourth aim defined for this thesis is to indirectly reduce the production of waste and the

consumption of virgin raw material by giving its reader a deeper understanding of the concept and

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process of deconstructing, and suggesting it as a solution for forthcoming construction or demolition

works;

The last and most ambitious aim is to seek a unique information technology solution that can

contribute to solving the issue of premature end of life of building elements;

1.4. Methodology

In order to know in detail the current situation of Deconstruction and what it involves the defined

research methodology is set to rely on two pillars:

A literature research of the state of art on the subjects of Deconstruction and Sustainability based

on published articles, conference reports, reports, books, internet sites and contact through email and

phone calls with field experts.

Beyond the search that is set to focus in published information, the methodology relies also on

attempting to consult the portuguese Construction industry and Deconstruction related companies in

order to gather their testimony on what have been their Deconstruction related practices. A total of

seventy-two emails were sent to entities from the above mentioned groups while in phase of literature

review of this thesis. The template for the email can be consulted on Appendix J. For the strategy

defined for this methodology to have an effect, at least 10 successful interviews need to be conducted.

1.5. Structure

The final object of this thesis is Deconstruction and the various ways in which it relates to

constructions along their Lifecycle. But to directly approach Deconstruction without relating to its

surrounding environment would seem unnatural. For the given reason, after the introductory chapter of

this document, this thesis addresses Sustainability. Due to the identified lack of information technology

in the field of Deconstruction, after studying it in a dedicated chapter, this thesis changes its focus to

creating a conceptual solution.

In the introductory chapter the reader is briefed with the authors overviewing concerns about the

non-changing mindset of humanity. The ambit in which he became in contact with the concept of

Deconstruction and simultaneously found interest in it is explained right after, which leads the reader

to this sub-chapter. The object of the study explains the structure of the dissertation; it is the thread of

thought that links this document together. On this sequence, there is a framing of how Deconstruction

is related to constructions, its connections to Demolition and to Recycling. The three ways to use the

term Deconstruction are explained. Following, the aims of this study are stated and its methodology is

explained. Some previous notes are given and a bibliographic review is made before entering the

beginning of the study.

The body of this thesis is Sustainability in Construction, and its explored core is Deconstruction.

The third chapter surveys this body by defining its main problem CD&W, assessing its legal framework

and what milestones are set to resolve it. Various aspects of Sustainability in Construction are

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analyzed such as Eco-efficiency, Embodied Energy, Lifecycle Assessment and Green Building

Certification.

The core is explored on the following chapter. The term Deconstruction is further explained and

Deconstruction’s historical development is framed. The current situation of Deconstruction is made in

an international review, and some practical recent cases are shown while using an author created

distinction for Deconstruction related practices. Various aspects linked to the practice of

Deconstruction’s activities are discussed, such as its principles, the variables for its choice, the design

for deconstruction, specific equipment and legal support.

Having a body and core, the last chapter before conclusions can be viewed as a member. The

perception that there was a lack of information technology applied to the Deconstruction industry gave

the author the idea to conceptualize a platform to support Deconstruction. This chapter consists in the

mentioned conceptualization.

1.6. Previous notes

The term Deconstruction isn’t solely reserved to the meaning of which this thesis document uses

it mostly. It was used by French philosopher Jacques Derrida in on 1967 in his work Of

Grammatology, defining Deconstruction as a way of criticizing not only both literary and philosophical

texts but also political institutions through which it was intended to be impossible to demonstrate a

strict interpretation of texts (the conflict between the various possible meanings of the same word).

While conducting investigation on Deconstruction other meanings can be found for the term

Deconstruction, even if searching for both terms “deconstruction” and “constructions” at the same

time, the results may be different from the expected. A common example is to stumble upon results of

the works by Christopher S. Butler and Javier Martín Arista, Deconstructing Constructions, which

refers to Construction Grammar approaches and the roles these constructions play in the frameworks

which can be located within a multidimensional functional-cognitive space.

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2. Sustainability in Construction

The term sustainability can be obtained by agglutination of the terms ability and sustainable.

Sustainability can therefore be considered as the ability to be sustainable. While the term ability is self-

explanatory, the term sustainable refers to the ability to survive without consuming more resources

than those which are produced. Something sustainable is something that can survive without

exhausting the provision of resources from the environment where it gathers them added to the

resources it produces on its own. Opposed to the term sustainable, something unsustainable is

something that in given time will deplete its source.

In construction, however, there is no creation of resources. The Construction industry is an

industry of resource consumption and transformation. Construction by itself will not reset the

resources consumed. The Construction industry can only be considered sustainable when analyzed in

conjunction with its constructions lifecycle. To fully assess sustainability in construction, it is necessary

to evaluate the amount of resources saved from raw natural extraction or production of waste over the

life of the construction works, the Lifecycle Assessment. Therefore, the role of sustainability in

construction is a global role, evaluating not just the consumption of resources during the act of building

or demolishing, but also the environmental impacts of the given construction along its lifetime.

2.1. Initial considerations

Europe has enjoyed many decades of growth in wealth and wellbeing, based on intensive use of

resources. But today it faces the dual challenge of stimulating the growth needed to provide jobs and

well-being to its citizens, and of ensuring that the quality of this growth leads to a sustainable future

(European Commission, 2011).

The growing consumption of raw materials observed in recent decades has generated resource

scarcity. Although there has also been an increase in the concern to reduce resource consumption

(Global Reporting Initiative, 2010/11), the consumption rate remains well above the replacement rate

by nature. According to (FootprintNetwork, 2014), the planet is currently consuming one and a half

times the amount of resources that can replenish. The forecast for 2050, if the estimated consumption

rate growth is kept, is that this planet is to consume close to triple the capacity of its renewal. (Julian

M. Allwood, 2010). This scarcity of resources not only can be scientifically analyzed via consultation of

documentation but is also empirically visible by the increasing price of raw material, which makes

sense due to reduced supply.

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Figure 1 - Current and estimated population resource consumption in comparison to the world's resource regeneration (source: (FootprintNetwork, 2014)).

Increased production of waste comes as a direct consequence of the increase in raw material

consumption. The existing ecological deficit is coming closer to exhaust the productive capacity of

nature, and its absorptive capacity of residues. Due to the community concerns regarding

environmental impacts in developed areas, it is now more complicated to create new landfills. On the

other side, location of landfills in remote locations increases transportation costs and energy use.

The increase of resource consumption and waste production is very much attributable to the

construction industry. It is responsible for creating about 40 percent of the waste emissions worldwide

(Udayangani Kulatunga, 2006). According to (Torgal & Jalali, 2007), the C&DW represent one third of

the waste produced in the European space, approximately 500 Mt in the date of the study (2007). In

Portugal, about 4.4 Mt were estimated to have been produced during 2004, which could be reused

and from which 95 percent went to landfill.

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Figure 2 -Current resource consumption in Portugal (source: ( (FootprintNetwork, 2014)).

The population growth, economic growth and increasing purchasing power are aspects that are

directly involved in the increase of waste and resource consumption, and are indirectly leading

civilization to a scenario of unsustainability. To counteract this trend, this dissertation studies an

efficient way to handle waste from construction and demolition, reducing the typically high energy

costs of recycling processes.

2.2. Definition and characterization of C&DW

Different definitions are applied throughout the EU, which makes cross-country comparisons

cumbersome. In some countries even materials from land levelling are regarded as construction and

demolition waste (European Comission, 2014). The main difference between these definitions

concerns the intended destination of a material; the intended destination of a material is the decisive

factor in the OECD definition (Organisation de Coopération et de Développement Economiques,

1998).

In Portuguese legislation, according to Decree-Law No. 178/2006, of September 5th, waste is "any

substance or object which the holder intends to discard or is required to do so, particularly those

identified in the European List of Waste".

According to the European List of Waste, which was transposed into Portuguese law the March 3,

2004 under the decree 209/2004, the C&DW are composed of:

• Concrete, bricks, tiles and ceramic material;

• Wood, glass and plastic;

• Bituminous mixtures, coal tar and some tar products;

• Metals (including their alloys);

• Soil (including excavated from contaminated sites), gravel and dredging sludge;

• Isolation materials;

• Construction and demolition waste mixtures;

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A study made from the enquiry of construction industry companies on the northern coast side of

Portugal (L. Pereira, 2002) gathered information on the amounts of waste produced by each company.

One of the verified conclusions of this study was that most of the enquired companies didn’t have or

didn’t provide information, having received only 8.8 percent of answers for the enquiry, which only half

included quantified information.

Table 1 - Composition of C&DW as percentage by weight (source: (L. Pereira, 2002)).

Waste Composition % by weight

Concrete, masonry and mortar 35

Wood 5

Paper and carton 1

Glass 0,5

Plastics 1

Metals (including steel) 5

Excavation soils and gravel from the restoration of pavements 40

Asphalt 6

Dredging and drilling sludge 5

Other waste 1,5

The heaviest slice of the C&DW comes from soils, which are mostly generated from site

preparation and excavation works. Solis are generated in significant amounts and unless they can be

reused on the worksite they were dug from they’re destined to landfill.

The second heaviest slice corresponds to inert materials where concrete is included. Concrete is

known as the most widely produced construction material (J. Selih, 2007), being present in large scale

constructions e.g. dams, skyscrapers, bridges, and being very popular in big cities who are nowadays

given the nickname of “concrete jungles”. Most of the portuguese buildings that were built before the

concrete era had a masonry/wood structure, which make their demolition provide a great amount of

waste in this segment and also in the wood segment. Mortars usually come in mixed with bricks,

concrete or wood, they are mostly used as isolation and finishing materials, and so they are not easily

detached from their support.

These aggregate wastes can be composed of different mixtures, in a conference report by (J. de

Brito, 2007), evidence is provided to conclude that a clean mixed aggregate can be charged as much

as 30 times less to recycle than a contaminated mixture containing any kind of low density non-

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hazardous contaminants. Appendix A provides the information on the fees of recycling C&DW charged

by a recycling company called Trianovo.

Asphalt waste originates essentially from the demolishing or rehabilitation of pavements. New

pavements can include all sorts of recycled materials besides asphalt, from inert construction debris to

steel slags (Marques, 2009). Due to its impermeability it can also be found on ceilings or retaining

walls.

As stated above, in Portugal wood waste can originate in great quantities from old buildings dated

pre 1930’s. These had structural walls, wall coatings, floors and floor structures made of wood, as well

as window frames and doors. Wood mixtures such as OSB or plywood can too be found, especially in

newer construction elements. Of the known problems about wood wastes are the fact that wood has

low resistance to biologic degradation (fungal and insect attack) (Torgal & Jalali, 2011) and that wood

elements frequently contain steel nails that weren’t correctly removed, or may have been subject to

treatments to increase durability or to make them more resistant to pests. These treatments may

include potentially environmental hazardous products such as led based paints.

Since the 1980s, the construction industry has benefited from faster construction techniques

based on steel frames (Symonds, ARGUS, 1999). Structural steel can also be found in reinforced

concrete structures, window frames and electrical equipment, generally in greater amounts on recent

construction than in old stone masonry structured constructions.

Plastic in C&DW can be found as different polymers, such as Polyethylene terephthalate (PET),

High density polyethylene (HDPE), Low / linear low density polyethylene (L/LLDPE), Poly‐vinyl

chloride (PVC), Polypropylene (PP), Polystyrene (PS), expanded polystyrene (EPS), Polyurethane

(PU), Nylon and other aggregated polymer types (Plastics and Chemicals Industries Association,

2011–12). Plastics are generated by a polymerization of basic molecules (monomers), creating long

chain monomers, which fall into two main categories, thermoplastics and thermosetting plastics.

Thermosetting plastics are supplied as fluid products and gain their shape by chemical reaction or

when submitted to temperatures above 200ºC. Thermoplastics are the conventional plastics that are

supplied ready to be used. Their shape can be worked by applying temperature. Examples of

thermoplastics are PVC, polyethylene, polypropylene or polystyrene (Torgal & Jalali, 2011).

Paper and carton, while representing only one percent by weight of C&DW are more commonly

present on constructions than on demolitions. Most of this waste comes from the packaging and

conditioning of construction materials.

Glass, while weighing only about 0,5 percent of C&DW is found on windows, skylights, handrails

and fixed furniture. It’s a highly recyclable material, and its removal should be done as one of the first

demolishing activities. Due to its frailty, this type of waste has to be dealt with enhanced care, since its

fragments can be dangerous to the work environment.

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2.3. Potential environmental impact of C&DW

Some of the materials that are included in C&DW are considered as hazardous. The application

of inadequate practices for the management of C&DW such as their disposal to uncontrolled sites or

the use of inefficient procedures during their management can lead to the release of these

substances/materials to the environment, causing negative environmental impacts. Research presents

that the leachate from land filled by solid waste from construction and demolition activities poses a

potential risk to groundwater quality (Chunlu Liu, 2007).

The European List of Wastes (European Commission, 2000) defines in the C&DW class the

following as hazardous wastes pursuant to Directive 91/689/EEC on hazardous waste and subject to

the provisions of that Directive unless Article 1(5) of that Directive applies.

Table 2 - Hazardous C&DW in the European List of Wastes (source: (European Commission, 2000)).

17 CONSTRUCTION AND DEMOLITION WASTES (INCLUDING EXCAVATED SOIL FROM CONTAMINATED SITES)

17 01 06* mixtures of, or separate fractions of concrete, bricks, tiles and ceramics containing dangerous substances

17 02 04* glass, plastic and wood containing or contaminated with dangerous substances

17 03 01* bituminous mixtures containing coal tar

17 03 03* coal tar and tarred products

17 04 09* metal waste contaminated with dangerous substances

17 05 03* soil and stones containing dangerous substances

17 05 05* dredging spoil containing dangerous substances

17 05 07* track ballast containing dangerous substances

17 06 01* insulation materials containing asbestos

17 06 03* other insulation materials consisting of or containing dangerous substances

17 06 05* construction materials containing asbestos

17 08 01* gypsum-based construction materials contaminated with dangerous substances

17 09 01* construction and demolition wastes containing mercury

17 09 02* construction and demolition wastes containing PCB (for example PCB-containing sealants, PCB-containing resin-based floorings, PCB-containing sealed glazing units, PCB-containing capacitors)

17 09 03* other construction and demolition wastes (including mixed wastes) containing dangerous substances

While deconstructing a building, there is a high probability of having to deal with some of these

wastes as well. Asbestos became one of the major concerns nowadays regarding hazardous wastes.

A scientific report states that the asbestos cancer epidemic may take as many as 10 million lives

before they’re banned worldwide and exposures are brought to an end. Five to seven percent of all

lung cancers can be attributed to occupational exposures to asbestos (LaDou, 2004). Recent media

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reports state that in Portugal there are still about 800 public buildings containing asbestos such as

schools and universities (Expresso, 2014).

Portugal had the implementation of laws regarding the use or commerce of asbestos containing

products since 1987. Through time an increase of the limitations of the use of this product were made,

and on 1991 it was prohibited by the Decree-Law No. 101/2005 of the 23rd of June. A great relevance

is given to protection equipment on worksites containing asbestos. A more detailed exposure of the

portuguese law regarding asbestos may be found in the portuguese governmental website (Governo

de Portugal, 2014).

Thermosetting plastics are also environmentally hazardous. They include polyurethane, which is

obtained from isocyanides, a substance that is highly toxic and there are records of serious health

problems in workers using polyurethane (The National Institute for Occupational Safety and Health,

1996).

2.4. Legal framework on C&DW

Sustainability consciousness led to the creation of some necessary laws to achieve a better

management of waste and reduce its production. In the construction sector, these laws were first

elaborated at an European scale, and afterwards were transposed to portuguese law.

Ahead, we have a chronological exhibition of both portuguese and european laws, indicating the

progress of the concern for sustainability in building materials.

2.4.1. Legal framework in Europe

The European Economic Community Directive No. 75/442 / EEC was issued on the 15th of July,

1975, setting the foundations for waste management. Three years later, the directive No. 78/319 /

EEC of the 20th of March, defined specific details to hazardous waste limits.

In the 90’s decade the Directives No. 91/156 / EEC of the 18th of March and No. 91/689 / EEC of

the 12th of December establish the maximum degree of environmental protection through the creation

of Waste Management Plans. With aim to improve the disposal of hazardous waste these Directives

include the definition of the new categories of waste, and the Community’s new measures are

clarified. The European Waste Catalogue and Hazardous Waste List are approved in December 1993,

which will later be revoked by the Decision No. 96/350 / EC of the 24th of May, where the recovery

operations of waste is going to be classified.

The Decision No. 2000/532 / EC of the 3rd of May, revokes the List of Hazardous Wastes and the

European Waste Catalogue, which are then reformed by the Decisions No. 2001/118 / EC of the 16th

of January and No. 2001/119 / EC of the 22nd of January, and 2001/573 / EC of the 23rd July.

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The Directive No. 2006/12 / EC of the 5th April, proposes a common terminology for the definition

of waste by implementing regulations on the disposal and recovery of waste and moveable assets.

Subsequently, a revision of Directive No. 2006/12 / EC of the 5th April, by the Directive No.

2008/98 / EC of the 19th November was made in order to minimize the negative effects of the

generation and management of waste on human health and on the environment. In this review there

were also created targets for reuse and recycling, determining the base value of 70 percent by weight

for reuse, recycling and recovery of non-hazardous RCD to be achieved until 2020. The Directive No.

2008/98 / EC of the 19th November, revokes the Directives No. 75/439 / EEC, No. 91/689 / EEC and

No. 2006/12 / EC mentioned above.

2.4.2. Legal framework in Portugal

With the objective to pursue a strategy to encourage the decrease of waste production, the

Decree-Law No. 488/85 of the 25th November laid the foundations for compulsory registration of waste

and defined the powers and responsibilities in the field of waste management. This decree resulted

from the transition from Directive 75/442 / EEC of 15 July for national legislation.

Ten years later the Decree-Law No. 488/85 of the 25th November is revoked by the Decree-Law

No. 310/95 of the 20th November. This new law, by transposition of Directives No. 91/156 / EEC of the

18th March and No. 91/689 / EEC of the 12th December, establishes the regulations regarding waste

management, including collection, storage, transportation, treatment, recovery and disposal. The

Regulation of Transport of Waste in the National Territory is created by the No. Decree 335/97 of the

16th May. This regulation introduces the Waste Accompaniment Document (in Portuguese: GAR -

Guia de Acompanhamento de Resíduos), which will later adapt to the electronic format (e-GAR) and

sets the standards for waste transport.

The Decree-Law No. 310/95 of the 20th November, is redesigned two years later by the Decree-

Law No. 239/97 of the 9th September, in which there are introduced some improvements, such as prior

authorization of waste management operations and making the licensing activities involving operations

of waste management more understandable for the involved entities.

In 1997, the Strategic Plan for Municipal Solid Waste (in Portuguese: PERSU – Plano Estratégico

para os Resíduos Sólidos Urbanos) was approved, in which the RCD are allocated in one of nine

categories of waste that constitute the urban solid waste section. PERSU is updated in 2007 to remain

effective for the period 2007-2016 (PERSU II), through Ordinance No. 187/2007, of the 12th February,

aiming to establish the main vectors in municipal solid waste management strategy in accordance with

the law and community framework, correcting the fundamental weaknesses demonstrated by PERSU.

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The strategic guidelines for the management of municipal waste set by PERSU are:

• Reduce, reuse, recycle;

• Separate at the source;

• Minimize landfill deposit;

• Maximize the energy recovery of non-recyclable fraction;

• Use the "Kyoto Protocol" commitment as determinant in waste policy;

• Validated information in time to be able to make decisions;

• The sustainability of urban waste management systems;

In 1999, the Strategic Plan for Industrial Waste Management (in portuguese: PESGRI - Plano

Estratégico de Gestão dos Resíduos Industriais) is approved through Decree-Law No. 516/99, of the

2nd December, defining the strategic principles of waste management adapted from the Community

Strategy of Waste Management, adopted by the Resolution of the Council of Ministers of the

European Union on the 24th February 1997.

On PESGRI, the C&DW are presented as industrial waste, elaborating the main goals in

managing this type of waste. PESGRI has the fundamental objective to define the principles in the

hierarchy of waste management, i.e. prevention, recycling, recovery and disposal as the final

destination, when all other possibilities are exhausted. With this plan arises the responsibility that all

stakeholders have in the lifecycle of a product and in its scrupulous management, with greater

importance attributed to the product manufacturer. The most important purpose of this plan is to

reduce the amount of hazardous and industrial waste through prevention.

In the sequence of PESGRI, the creation of the National Plan for Prevention of Industrial Waste

(in portuguese: PNAPRI - Plano Nacional de Prevenção de Resíduos Industriais) was proposed. This

is a planning tool for Public Administration and all economic agents, aiming to reduce the amount of

hazardous and industrial waste through prevention measures and technologies associated with

industrial processes.

Subsequently, the Decree-Law No. 3/2004, of the 3rd of January, is published and defines the

legal regime of licensing, installation and operation of Integrated Waste Rehabilitation, Recovery and

Hazardous Waste Disposal Centers (in portuguese: CIRVER - Centros Integrados de Recuperação,

Valorização e Eliminação de Resíduos Perigosos).

Afterwards, the European List of Waste List is approved, through Ordinance No. 209/2004 of the

3rd of March, simplifying the process of disposal and recovery.

Later, the Decree-Law No. 239/97, of the 9th of September, is revoked by the Decree-Law No.

178/2006, of the 5th of September, establishing the new legal regime regarding the management of

waste. This last Decree transposes into Portuguese law the Directive No. 2006/12 / EC of the 5th of

April, and presents the definition of construction and demolition waste for the first time in Portuguese

law. This legislation aims to establish principles for waste management promote the association of

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new instruments in the national legal framework and also introduce new economic and financial

concepts of waste management as an organized waste market with demand and supply of materials in

way that is safe, effective and fast.

Within the General Regulation of Waste Management (in portuguese: RGGR – Regime Geral da

Gestão de Resíduos), elaborated from the Decree-Law No. 178/2006, of the 5th of September, is the

Integrated Waste Electronic Journal (in portuguese: SIRER - Sistema Integrado de Registo

Electrónico de Resíduos), which is regulated by Portaria No. 1408/2006 of the 18th of December, and

which establishes the obligation of the entities responsible for specific waste streams, integrated or

individual, to fulfill the completion of specific registration systems, whose content focuses on the object

of activity’s permit or license. In the given year, some technical specifications were released by the

National Laboratory of Civil Engineering: the guide to the use of recycled coarse aggregate concrete

with hydraulic binders (E 471-2006); a guide to recycling of bituminous mixtures in the hot core (E

472-2006); a guide to the use of recycled aggregates in unbound pavement layers (E 473-2006); and

a guide to the use of RCD in landfill and bed transport infrastructure (E 474-2006) layer.

One year after, the Legal System of Urbanization and Construction (in portuguese: RJUE -

Regime Jurídico da Urbanização e Edificação) is established, through Law No. 60/2007, of the 4th of

September, referring the Regulation of Management of Construction and Demolition Waste (in

portuguese: RGRCD - Regime da Gestão de Resíduos de Construção e Demolição) on some articles

of this law.

Then, the new Code of Public Contracts (in portuguese: CCP – Código dos Contractos Públicos)

is presented in the Decree-Law No. 18/2008, of the 18th of January, referring several times the

importance of the Plan for the Prevention and Management of Construction and Demolition Waste (in

portuguese: PPGRCD - Plano de Prevenção e Gestão de Resíduos de Construção e Demolição) in

the management of RCD on several of its articles. The Decree-Law No. 46/2008, of the 12th of March,

defines the prevention and reuse, and the operations of collection, transportation, storage, sorting,

treatment, recovery and disposal of C&DW on the Regulation of Waste Management Construction &

Demolition. The existence of this regulation regards the determination of methodological rules related

to management procedures of C&DW, in accordance with the Article 20 of Decree-Law No. 178/2006,

of the 5th of September, ensuring employment of management policies of C&DW like recycling, reuse

and waste reduction.

In 2008 some adjustments are introduced to the Decree No. 335/97 of the 16th of May, when the

models of CD&W Monitoring Guides (in poruguese: GARCD - Guias de Acompanhamento dos

Resíduos de Construção e Demolição) are approved through Portaria No. 417/2008, of the 11th of

June, which will define the specific guides to use in the transportation of C&DW.

The Decree-Law No. 46/2008, of the 12th of March, established the specific legal regime to which

are subject the resulting wastes from constructions, demolitions or landslides.

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The Decree-Law No. 183/2009 of the 10th of August, reinforces the principle of hierarchy of waste

management, establishing legal system of waste disposal in landfill, the general requirements to be

fulfilled in the design, construction, operation, closure and post-closure of landfills.

Subsequently, the regime of formation, management and operation of the waste market is

established by Decree-Law No. 210/2009, of the 3rd of September, with the aim of correcting the gaps

of the standardization processes needed related to monitoring and inspection actions, the

management of waste entities and markets. This Decree aims to establish a bridge between electronic

platforms of organized waste markets and the Integrated Registration Platform of the Portuguese

Environment Agency (in portuguese SIRAPA - Sistema Integrado de Registo da Agência Portuguesa

do Ambiente).

Later, the Portaria No. 228/2010, of the 22nd of April, shows the logo of the Organized Waste

Market (in portuguese MOR - Mercado Organizado de Resíduos) to be used by trading platforms of

waste management (Figure 3).

Figure 3 - Logo of the Organized Waste Market (source: (Mercado Organizado de Resíduos, 2014)).

Recently, the Decree-Law No. 73/2011, of the 17th of June, amending the legal framework for

waste management transposes the Directive No. 2008/98 / EC of the 19th of November. This aims to

clarify key concepts such as the definitions of waste prevention, reuse, preparing for reuse, treatment

and recycling, and the distinction between the concepts of recovery and disposal of waste, based on

an effective difference in environmental impact and also taking into account the waste hierarchy as a

fundamental principle of environmental policy. This legislation amends the Decree-Law No. 178/2006

of the 5th of September, and No. 46/2008, of the 12th of March.

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The Decree-Law No. 73/2011, of the 17th of June, sets goals for the recycling of MSW and its

recovery for the horizon 2020 and obliges, when technically feasible, the use of 5 percent recycled

materials from the total of raw materials used by the construction industry. Among other measures,

this Decree also introduces the electronic guide for electronic waste monitoring (e -GAR), the

mechanism of the producer’s extended responsibility, and defines the order of priorities regarding to

waste prevention and management options:

• Prevention;

• Preparation for reuse;

• Recycling;

• Other types of recovery;

• Elimination.

According to the same Decree-Law, the responsibility for waste management "is given to the

original waste producer, without prejudice that it can also be attributed, in whole or in part, to the

producer of the product from which the waste was originated, and the responsibility can be shared by

the distributors of such product if such should occur from specific legislation.”

The most recent legal publication on C&DW is the Portaria No. 40/2014 of the 17th of February,

which establishes the norms for correct removal of asbestos containing waste and its management

and transportation, having as the greater concern the environment and human health.

2.5. Milestones for Sustainability

In order to gradually reduce the production of waste, Europe has defined milestones, setting goals

for the various types of waste. According to (European Commission, 2011), the Waste Framework

Directive (WFD) requires Member States (MS) to take any necessary measures to achieve a minimum

target of 70 percent (by weight) of C&D waste by 2020 for preparation for re-use, recycling and other

material recovery, including backfilling operations using non-hazardous C&D waste to substitute other

materials.

One of the milestones set is that by 2020 waste is managed as a resource. Waste generated per

capita will be absolute decline. Recycling and re-use of waste will be economically attractive options

for public and private actors due to widespread separate collection and the development of functional

markets for secondary raw materials. More materials, including materials having a significant impact

on the environment and critical raw materials will be recycled.

Waste legislation is set to be fully implemented. Illegal shipments of waste have been eradicated.

Energy recovery will be limited to non-recyclable materials, landfilling will be virtually eliminated and

high quality recycling will be ensured.

By 2020, scientific breakthroughs and sustained innovation efforts are set to have dramatically

improved how we understand, manage, reduce the use, reuse, recycle, substitute and safeguard and

value resources. This will have been made possible by substantial increases in investment, coherence

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in addressing the societal challenge of resource efficiency, climate change and resilience, and in gains

from smart specialization and cooperation within the European research area.

A major shift from taxation of labor towards environmental taxation, including through regular

adjustments in real rates, will lead to a substantial increase in the share of environmental taxes in

public revenues, in line with the best practice of Member States.

By 2020 the renovation and construction of buildings and infrastructure will be made to high

resource efficiency levels. The Life-cycle approach will be widely applied; all new buildings will be

nearly zero-energy and highly material efficient and policies for renovating the existing building stock

will be in place so that it is cost-efficiently refurbished at a rate of 2 percent per year. 70 percent of

non-hazardous construction and demolition waste will be recycled.

By 2050 the EU's vision is for its economy to have grown in a way that respects resource

constraints and planetary boundaries, thus contributing to global economic transformation. Our

economy is competitive, inclusive and provides a high standard of living with much lower

environmental impacts. All resources are sustainably managed, from raw materials to energy, water,

air, land and soil. Climate change milestones have been reached, while biodiversity and the

ecosystem services it underpins have been protected, valued and substantially restored.

In Portugal, the Strategic Plan for Municipal Waste (Portuguese Environmental Agency, 2014)

aims to achieve the following goals by 2020:

Have waste managed as endogenous resources, minimizing their environmental impacts and

taking advantage of its socio-economic value.

Have an efficient use and management of primary and secondary resources, decoupling

economic growth from material consumption and waste production.

Progressive elimination of waste disposal in landfill, with the eradication of direct deposition of

urban waste on landfill by 2030.

Harnessing the potential of the urban waste sector to stimulate local economies and the

national economy: an added value activity for people, for local authorities and for businesses,

with the capability of internationalization in the context of a green economy.

Direct involvement of the common citizen in the urban waste strategy, focusing on information

and facilitating the reduction and separation, with a view to recycling.

2.6. Hierarchy of waste management in Construction

Construction and demolition waste has been identified as a priority waste stream by the European

Union. There is a high potential for recycling and re-use of C&DW, since some of its components have

a high resource value (European Comission, 2014).

Of the many possible solutions that can be given to construction waste, some more efficient than

others, the best environmental and cost effective solution is to reduce the amount of waste created.

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Reducing can be made by preventing unnecessary waste, source waste reduction or resource

optimization.

Although (Mark D. Webster B. M., 2005) states that reuse is the most desirable option because it

is most effective in reducing the demand for virgin resources and reducing waste, in this thesis authors

opinion, reusing materials has the added challenge of deconstruction, storage and adaptation. One

can’t say that deconstructing and reusing will be more or less effective than any other solution,

because it greatly depends on case specific variables.

Recycling demands complex industrial processes. The amount of consumed energy depends on

the type of material that is recycled. For recycling to achieve its maximum efficiency, the waste has to

be separated with a great care. In the same way that reusing’s costs depend on a large number of

variables, so does recycling. Recycled materials can result in more or less valuable materials than its

source. These processes are called “upcycling” and “downcycling”.

Figure 4 - Waste Management Hierarchy for demolition and construction operations (CHARLES J. KIBERT, 2001).

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2.7. Eco-efficiency

In the common thought the concept of sustainability decouples from economic growth. In general,

it is believed that a product created with the concern that its production does not disturb the

environment is a product that requires an extra effort in their production process, and as such, a price

increment. -Examples of not construction related industries can be easily found, such as food or

consumer goods industries. As an example, a food product that comes from organic farming is

typically more expensive than the similar product coming from conventional production. In order to

boost economic growth, sustainability is often a sidelined idea, since there is this stigma that it isn’t

cost effective.

Eco-efficiency is a management philosophy that encourages business to search for environmental

improvements that yield parallel economic benefits. It focuses on business opportunities and allows

companies to become more environmentally responsible and more profitable. It is a key business

contribution to sustainable societies (Katherine Madden, 2005). Eco-efficiency is also a goal for

society in general. It is recommended by intergovernmental organizations and adopted by many

countries as the most promising policy towards sustainable development.

Eco-efficiency is achieved by profound changes in the goals and assumptions that drive corporate

activities, and change the daily practices and tools used to reach them. This means a break with

business-as-usual mentalities and conventional wisdom that sidelines environmental and human

concerns (Schmidheiny, 1992).

Currently, eco-efficiency represents one of the great challenges of Deconstruction. It isn’t enough

just to get the process to become ecologically sustainable, it’s also important to ensure its economic

sustainability. In specific cases where the works of demolition and construction are geographically

close and its timeline plans are work compatible, it is easy to assume that Deconstruction is eco-

efficient. Even so, it’s still necessary for both entities involved in the demolition and construction

processes to be aware of both works, and willing to cooperate with each other, which can be facilitated

with the use of electronic platforms. In the general case, however, for Deconstruction to be profitable,

the use of technological developments won’t be enough, the conventional mindset linked to traditional

demolition needs to change and gradually adapt to the philosophy of re-utilization of construction

materials.

2.8. Embodied energy concept

In order to build with the concern of sustainability there is a need to objectively measure the

environmental effects caused by the construction. While there are tools for analyzing the lifecycle of a

building (LCA) and certification systems for assessing the buildings sustainability they rely on the

amounts of energy that was spent on the creation of the materials that compose the building.

On a generic definition, energy analysis is the process of determining the energy required directly

and indirectly to allow a system to produce a specified good or service (M.T. Brown, 1996). Embodied

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energy, is the total amount of energy required to produce a product (Graham F. Treolar, 2001). These

energy analyses include the energy cost of the entire lifecycle process chain from raw materials

extraction and transportation, transformation, use and the recycling and disposal stages following

actual use. A less frequent approach on the lifecycle costs of a given product is the Embodied Carbon,

which measures the carbon emitted into the atmosphere during the products lifecycle (Building Green,

2014). Analyzing embodied carbon and embodied energy levels of a given material would be

redundant, since both values can be arithmetically converted into each other.

Table 3 – Average embodied energy in construction materials (source: (Andrew Alcorn, 1998)).

Material Embodied energy

MJ/kg MJ/m

Cement, average 9.0 17550

Ceramic brick, old technology 7.7 1580

Concrete block-fill 1.4 3150

Earth rammed soil cement 0.73 1450

Insulation wool (recycled) 20.9 200

Stainless steel, average 50.4 395640

Timber: kiln dried, average, dressed

5.09 2200

Water, reticulated 0.003 3.3

Another important aspect to have into consideration while evaluating the embodied energy of the

materials used in a construction is the energy spent on transportation, which will depend on the

chosen transportation and the density of the analyzed material.

Table 4 -Energy consumption in transport (source: (Berge, 2009)).

Type of transport Energy consumption (MJ/ton km)

By air 33–36

By road, diesel 0,8–2,2

By rail, diesel 0,6–0,9

By rail, electric 0,2–0,4

By sea 0,3–0,9

The improvement in construction standards and tighter imposed regulations, are conducting to

higher energy efficiency. Some building elements such as photo-voltaic panels and solar thermal hot

water systems have achieved low to zero embodied energy levels due to the fact that during their

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lifecycle they can produce more energy than the energy spent on their production (Sanchez, 2008).

The use of these elements reduces the operational emissions associated with new buildings.

Deconstruction stretches the usage life of building materials. Although the costs of dismantling,

storage, and adaptation may be relevant, an objective notion of the amount of energy that can be

saved can be obtained by measuring the embodied energy on the amount of deconstructible materials

from a given demolition site. To do so, it should be taken into account the condition of the materials

and estimated their remaining usage life. A more complete list from (Andrew Alcorn, 1998) can be

consulted in Appendix C.

2.9. Lifecycle Assessment

Lifecycle Assessment is an important methodology for the evaluation of material and energy

fluxes and their impact on the environment. In most cases Lifecycle Assessment has been utilized on

industrial processes to determine the environmental impacts of the lifecycle of a specific product,

including an analysis of each stage of the product manufacture, transport, utilization and disposal

(Ilaria Principi, 2003).

According to (ISO14044:2006, 2006) lifecycle assessment (LCA) is the compilation and

evaluation of the inputs, outputs and the potential environmental impacts of a product system

throughout its lifecycle. The product’s lifecycle is defined as the consecutive and interlinked stages of

a product system, from raw material acquisition or generation from natural resources to final disposal.

Lifecycle Assessment (LCA) is a structured and internationally standardized method that

transposes Lifecycle Thinking (LCT) principles into a quantitative framework. LCA quantifies all

relevant emissions, resources consumed/depleted, and the related environmental and health impacts

associated with any goods or services. Therefore, within the concept of LCT, LCA is a vital and

powerful tool to effectively and efficiently help make consumption and production globally more

sustainable.

When LCT/LCA are applied to waste management services, typically the assessments focus on a

comparison of different waste management options, not covering the entire lifecycle of the products

which have become waste. Therefore, LCT/LCA applied to waste management services can differ

from product LCT/LCA. Product LCT/LCA accounts for the entire lifecycle of a product, in which waste

management may play only a minor role. However, if one of the evaluated waste management options

includes that materials are given back into the lifecycle of a product, a product lifecycle perspective

has to be taken into account also in LCT/LCA for waste management services. (Joint Ressearch

Centre, 2011).

Deconstruction can take part during the whole lifecycle of a construction. Buildings can be

designed from scratch with the intent to use recycled materials. During the the usage life of the

building, it can suffer adaptations, which may generate or consume reusable building elements. On

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the buildings end of life, Deconstruction is responsible for the collection of the buildings elements that

might fit on another construction taking place close by.

Although LCA creates a closed-loop lifecycle for a construction, it may not necessarily be realized.

Continual management is necessary in order to have a probability of success in implementing a

closed-loop lifecycle. To accomplish this it may be best to attach a Building Service Life Plan, a plan

that manages the performance requirements during the design life.

Figure 5 - Lifecycle of construction materials. (source: (Chunlu Liu, 2007)).

Some tools assess the lifecycle (LCA) of buildings while others assess the sustainability of

buildings such as the ones addressed on chapter 2.10. A more extent list of LCA tools, software and

databases for buildings is presented on Appendix C. Below is a list of the more commonly used LCA

tools:

Table 5 - Lifecycle Assessment Software and Databases (source: various documents and author-made research).

Designation Link

Athena Institute http://www.athenasmi.ca/

Building for Environmental & Economic Sustainability (BEES)

http://www.bfrl.nist.gov/oae/software/bees/

GREENCALC http://www.greencalc.com/

OpenLCA http://www.openlca.org/

SimaPro Life Cycle Assessment Software http://www.pre.nl/simapro/

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2.10. Green Building Certification

Buildings have both direct and indirect impacts on the environment. These impacts can occur

during their construction, occupancy, renovation, repurposing, and demolition. The energy spent, the

use of water and raw materials, the generated waste and potentially harmful atmospheric emissions

can be measured or estimated. These facts have brought the need to create green building standards,

certifications, and rating systems aimed at mitigating the impact of buildings on the natural

environment through sustainable design.

While building certification is an undeniable advance towards sustainability, there is a general

misuse of the expression “sustainable construction”. This term is usually applied to buildings that have

adopted some sustainable measures and are in fact “more sustainable than” they would be without

those measures. Even so, building construction is still characterized by a high ecological footprint

(Maria Emiliana Fortunã, 2012) and therefore still far from achieving the net zero ecological footprint

considered as sustainable.

Currently, the most implemented systems are the Building Research Establishment

Environmental Assessment Method (BREEAM), from the United Kingdom, the Leadership in Energy

and Environment (LEED), from the USA, and the French High Environmental Quality (HQE).

Table 6 - Green building certification systems, their origin and the entities who promoted their creation (source: various documents and author-made research).

Origin Designation Promoter

USA LEED US Green Building Council

USA ENERGY STAR® Green Buildings Institute

USA Green Globes US Environmental Protection Agency

USA Green Building Initiative Private investment

UK BREEAM Building Research Establishment

France HQE Scientific and Technical Centre for Buildings

Australia Green Star Green Building Council of Australia

Canada BOMA Go Green Plus Building Owners and Managers Association of Canada

Canada SB Tool Private investment

Germany Deutsches Gütesiegel Nachhaltiges Bauen

German Federal Ministry for Transport, Building and Urban Development

Japan Comprehensive Assessment System for Built Environment Efficiency

Japan GreenBuild Council

Portugal LiderA Private investment

Worldwide, there are many other green building rating and certification systems. Some aren’t

internationally applicable, but can be of influence in the green building certification industry.

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2.10.1. BREEAM

The BREEAM system is applicable on diverse situations, in its homepage (BREEAM, 2014)

claims to be able to assess any type of building anywhere in the world. There are BREEAM

communities that share developments and a BREEAM online portal called BREEAM Extranet, which

is used by licensed BREEAM Assessors. The BREEAM system works by giving credits to the building

when a given measure is taken. These measures have different values that depend on its contribution

to the building’s environmental impact reduction. They represent a broad range of categories and

criteria from energy to ecology, including aspects related to energy and water use, the internal

environment (health and well-being), pollution, transport, materials, waste, ecology and management

processes.

This system presents itself as a composition of instruments to be used by building contractors,

users and managers aiming to enhance the building’s environmental characteristics (Pinheiro, 2006).

The general approach of the BREEAM system is based in the following phases:

Initial assessment;

Scaling, Inventory and Purchase of Materials;

Management and Operation;

Quality Control;

BREEAM’s critics note that the credit system has flaws. They state that in a building where the

objective was to reduce the energy consumption and also meet BREEAM standards the assessor

wanted to install chilled water fountains. They argued that it would be illogical because it increases

energy consumption. Also, when incorporating reused materials in a construction (the example given

was the use of a refurbished steel frame), BREEAM is set up so that no added credits are given for

reusing a refurbished frame instead of using a new one (BDonline, 2014).

2.10.2. LEED

Leadership in Energy and Environmental Design was created by the US Green Building Council,

and is an also very well-known rating system for buildings. In the same way as BREEAM, its

framework consists of several rating categories, applicable to different points in a building’s lifecycle.

Each category is inserted in a LEED rating system. LEED NC and LEED EB for example, are

applicable to New Constructions and Existing Buildings and are both inserted in the Building Design

and Construction rating system. The cost to the project can depend on the rating system, the level of

certification sought and the experience level of the team.

Currently there are five LEED rating systems that address multiple project types:

BD+C – Building Design and Construction;

ID+C – Interior Design and Construction;

O+M – Building Operations and Maintenance;

ND – Neighborhood Development;

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HOMES – Homes;

The LEED NC category, as an example, includes a guide and a project checklist in which are

represented six general areas, being necessary to fulfill a set of pre-performance requirements, from a

total of 69 sub-items (specific areas) and some mandatory prerequisites (Pinheiro, 2006). The six

general areas presented are as follows:

Sustainable Sites;

Water efficiency

Energy & Atmosphere;

Materials and resources;

Indoor environmental quality;

Innovation;

Figure 6 - Six general areas of the LEED NC category, and their given weight (source: (Pinheiro, 2006)).

Upon scoring points in the given areas, its sum corresponds to a level of certification that scales

from a standard LEED certification through “silver, “gold” and “platinum”.

(U.S. Green Building Council, 2014) states that there seems to be a growing market acceptance

of LEED standards, and that the costs of certification are normalizing. In the USA, numerous

municipalities and government departments, including the General Services Administration, and an

increasing number of private investors and owners have instituted policies requiring LEED certification

for new construction projects.

Sustainable Sites; 20%

Water efficiency

7%

Energy & Atmosphere;

25%

Materials and resources;

19%

Indoor environmental

quality; 22%

Innovation;7%

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Depending on the project, energy related practices will contribute approximately 20-30 percent of

all available LEED points. Recent revisions to the LEED system are further increasing the number of

mandatory energy-related points required for basic certification.

2.10.3. HQE

High Environmental Quality certification is a comprehensive, multi-criteria approach that brings

together all of the stakeholders of a project. It puts energy efficiency, respect for the environment, and

the health and comfort of occupiers first (High Environmental Quality, 2014).

HQE certification is based on three principles:

Project owners set their own objectives.

No architectural or technical solution is imposed and the project team makes its own choices

to adapt them to the situation at hand.

Project management support enables all project stakeholders to get involved and meet the

goals set.

The assessment process is based on a new method that is compatible with international

indicators such as the Sustainable Building Alliance, CEN TC 350.

HQE’s evaluating criteria are defined in the DEQE (Explicit Definition of Building Environmental

Quality) reference document for environmental characteristics; it lists 14 targets divided into 2 areas

and four families. For each operation, the building owner selects the most relevant targets, defines the

quantitative and qualitative objectives relating to the selected targets and then studies the technical

solutions.

For certification to be assessed, HQE requires that a project must be in compliance with local

regulations, if any exist (accessibility, seismic standards, etc.).

HQE’s approach relies on an environmental management operation system (SMO - Système de

Management de l'Opération) establishing the implementation of responsibilities while using the

requirements defined at the origin of the project.

The renovation of a building can be certified by HQE Rénovation. This new framework, suitable

for this type of work addresses a building in its phase of deconstruction as well the phase of

rebuilding. The HQE approach adds value to buildings with respect to customers increasing demands,

offer a new mark in sustainable development. The certification provides a guarantee on the design

and is recognized by stakeholders in the building construction industry.

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2.11. Chapter remarks

Sustainability in Construction has a well-established set of tools; more so, the constant change in

the world’s mindset seems to be in the direction of sustainable development. The need of recognizing

a building’s sustainability and its materials Lifecycle environmental burden are now valued measures

that have become of interest to the private sector. A good local example is the portuguese buildings

sustainability certification system, LiderA.

Construction investors are still facing the paradigm between choosing to build cheaper but in a

less sustainable way or to invest more in constructions that will be adaptable to new needs while

requesting less from the environment. The present economic crisis, known previously in Portugal as

the real estate crisis, keeps pushing back the advances made by Sustainability. It is an arms duel that

will hopefully be finished when the crisis is gone.

One detected flaw that keeps Deconstruction underdeveloped is the lack of Deconstruction-

specific support in the legal system. The word Deconstruction isn’t referred in any law regarding

C&DW. Reusing C&DW is referred a few times, but always while “grouped” with recycling; meaning

that the same legal value is given for recycling waste or to reusing it. Further in this thesis a review on

legislation that indirectly supports deconstruction related activities is made on subchapter 3.10.

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3. Deconstruction in the Lifecycle of Constructions

3.1. Initial considerations

According to Antoine Lavoisier’s law, “nothing is lost, nothing is created, everything is

transformed”. In the traditional demolition method, the waste that results from the demolition works are

either transformed by a long time consuming decomposition process on a landfill or submitted to

incineration. Recycling started being used as common alternative in the 1970’s, and although having

its strengths and weaknesses, it can be considered that recycling is overall a more costly solution due

to its energy costs, and landfill a cheaper but more time demanding solution.

In the Deconstruction perspective, transformation can occur by removing an element from a

construction and inserting it as an element in another construction, without having the element

undergo decomposition. This activity of dismantling and rebuilding activity or process is named

deconstructing.

There are many published definitions of the term Deconstruction. The general definition given by

authors like (Bradley Guy, 2002) or (Lobato dos Santos, 2010) is to consider deconstruction to be “the

process of building disassembly in order to recover the maximum amount of materials for their highest

and best re-use”. Other publications like (Greer, 2005), (Macozoma, 2001) or the non-official but

largely consulted (Wikipedia, 2014) give the definition for deconstruction in a simpler manner as

“construction in reverse”. Both definitions are given to the word while expressing an activity or

process.

In Portugal, there have been recent studies related to Deconstruction, with highlighted emphasis

on the works of Prof. Armanda Couto, Prof. Saíd Jalali, and Prof. José Barroso de Aguiar from the

University of Minho, and Prof. Jorge de Brito and Architect António Lobato dos Santos from Instituto

Superior Técnico.

3.2. Application of the term Deconstruction

In Portugal, it can be assumed that the concept of Deconstruction is largely unknown both to the

general public, as well as the community of the construction sector (Armanda Bastos Couto, 2007).

Besides the general inertia to mindset change in the Construction industry sector, one of the reasons

that helps explaining this is the fact that, as stated before, the term Deconstruction has been claimed

in the past by Jacques Derrida on 1967 in his work Of Grammatology, defining Deconstruction as a

way of criticizing not only both literary and philosophical texts but also political institutions.

In resemblance of the word Construction, the term Deconstruction can be used to define the

economic sector of the “Deconstruction” of works, or the process or activity to “deconstruct”. To make

this distinction, when referring to the “Deconstruction” sector it’s often used the allocation of capital

letter on the proper name, and the lowercase letter designating the activity of “deconstructing” (Lobato

dos Santos, 2010).

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This study of the word is susceptible to various interpretations, but it is accepted that most uses of

the word "deconstruction" can follow the same lines used on the word "construction". While the

Construction sector defines the set of activities and entities linked together to perform the physical

joining of materials that give rise to a work of construction, the sector of Deconstruction will define the

same set of activities and entities linked to deconstruction works.

There are exceptions of application, while in a given context the word “construction” may refer to a

building in order to indicate something that was the result of a process of construction, it’s indicating

some object which has physical form and is physically present. That statement cannot be made by

similar application of the term deconstruction because the process of deconstructing causes a removal

of material. The result of a work of deconstruction isn’t a sole object but a set of construction materials

or construction elements which can’t be referred to as a deconstruction. Still, the process of

undergoing a deconstruction operation can be considered as a deconstruction, in the way a worksite

in which are taking place deconstruction activities can be referred as a “deconstruction”.

3.3. History of Deconstruction

Although the earliest documented manuals of deconstruction only start appearing in the early

90’s, the concept of “Deconstruction” is estimated to be almost as old as is it brother concept

“Construction”. Ever since mankind started building, we‘ve had the need to scavenge for materials,

and old abandoned constructions have been perfect sources.

Along history there are some well-known cases of construction materials reuse. The Romans are

believed to be the first civilization to commonly reuse materials in constructions. This activity started

on 3rd century and grew from then on alongside the progressive decline of the Roman Empire (Lobato

dos Santos, 2010).

After four centuries of active use, the roman Colosseum fell into neglect, and up until the 18th

century it was used as a source of building materials. Though two-thirds of the original Colosseum

were destroyed over time, the amphitheater remains a popular tourist destination, as well as an iconic

symbol of Rome and its long, tumultuous history (History Channel, 2014). On a visit to this site, the

author of this thesis was told by the official guide tours of the Roman Colosseum that the punctured

holes visible in the below picture corresponded to anchorage points of the marble coating that once

existed. The upper part of the pillars of the first floor, as well as the corresponding arcs don’t have

holes because they weren’t coated, their ornaments were directly worked on the structural stone

blocks.

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Figure 7 - Roman Colosseum's punctured pilars and walls. The holes were part of a original marble coating support mechanism (source: internet search).

The removal and reuse of roman construction materials was so extent that it gained its own

expression – spoila. In “Roman Arquitetural Spoila” (Kinney, 2001), the term is referred to as the name

for the ancient marble ornaments that were repeatedly encountered in secondary medieval settings.

The reuse of materials that originated from the Roman Empire was extent on the following

centuries. Rome was dismantled to build Constantinople, and the monuments of Constantine

dismantled to build those of Justinian, and so on for a millennium. The marbles were always reused

with immense care, for they could never be replaced. They represented a connection to Imperial

greatness, authority, and history that money could not buy. (Orthodox Arts Journal, 2014)

Another interesting case of antique deconstruction are the foundations of the Notre Dame

Cathedral, in which were found pieces of roman antique pillars.

Figure 8 - Constitutive elements of roman pillars used as foundations in Notre Dame's Cathedral (source: (Lobato dos Santos, 2010)).

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For the construction of the Aachen Cathedral, in the late VIII century D.C., the emperor Carlo

Magnus ordered for the retrieval of “adequate” columns in Rome, since he considered that there was

no existence of quality construction materials in the area.

Roman marbles can be found on Islamic monuments too. Given the fact that a large proportion of

once-Roman sites in North Africa, Spain, Syria, Anatolia and the homelands of Byzantium were under

Islamic control, a quick survey of early Islamic monuments demonstrates a devotion to marble spolia

at least as profound as that in the Christian West or Byzantine East (Greenhalgh, 2005).

3.4. International overview of Deconstruction practices

In 1999 a joint work from the Powel Center for Construction and the Environment form the

University of Florida and the International Council for Research and Innovation in Building

Construction created a workgroup with the aim to analyze and produce information regarding

Deconstruction and the way to turn the reuse of construction materials as a viable alternative.

During the meeting of CIB TG39 in Garston, Watford, U.K. there were made presentations from

Australia, Germany, Israel, Japan, The Netherlands, Norway, the U.K., and the U.S regarding the

Deconstruction practices of these countries. A paper by (Kibert, Chini, & Langue, 2001) reports a

summary of these presentations which is resumed bellow.

In Australia the deconstruction of 70 to 100 year old timber houses is a common practice with

about 80 percent of the materials being recovered and reused for renovation and remodeling of

existing homes or in the construction of new, replica housing. The relocation of houses is also a

common practice, with 1000 homes being moved in the Melbourne area each year out of a total

housing stock of 800000 units. For residential structures it is estimated that between 50 and 80

percent of the materials are recovered in the demolition process. The recovery of materials from

commercial buildings is significantly lower with a total recovery rate of about 69 percent (58 percent

reuse and 11 percent recycled).

In Germany, between 1991 and 1999 several case studies on Deconstruction were conducted

and revealed an exceptionally high recovery rate, in excess of 95 percent for many structures.

German studies that investigated deconstruction methods show that optimized deconstruction

combining manual and machine dismantling can reduce the required time for a conventional

deconstruction by a factor of 2 with a recovery rate of 97percent.

In the Netherlands strict government regulations ensure that about 80 percent of C&DW materials

are reused or recycled and used in other constructions, generally in creating materials for road base.

The Dutch law states that “dumping of reusable building waste is prohibited” thus forcing even higher

rates of recovery. Efforts were done to inform architects and other actors in the construction industry

about the potential for designing buildings for deconstruction.

In Norway between 25 and 50 percent of the 978000milion tons of demolition waste is estimated

to be recycled or reused in the Oslo region.

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According to (Tulay Esin, 2007), in Turkey, mostly in Istanbul’s outlying suburbs there are building

material collectors. The collected salvaged building materials are sold in open and semi-open

salvaged building material outlets. At these outlets, wood and PVC doors and windows, kitchen and

bathroom components, strips, tiles, plastic pipes, asbestos roofing sheets, wooden lath, and others

are sold, in good and bad shape, mostly to low income wage earners.

3.5. Recent Deconstruction

Documented examples of recent deconstruction works give different perspectives of ways to give

building materials or elements a new life. One of the difficulties in analyzing a deconstruction work is

the given fact that there are very distinct works of deconstruction, some are sources of construction

materials and others are the destination of used construction materials.

When involved in a deconstruction process, the destination for the scavenged materials can either

be previously determined, or the materials can remain in storage until a fitting construction is found. In

this sense, a deconstruction operation can be classified on the existence of the availability of a

material donating deconstruction worksite and the existence of a receiving construction for those

materials.

In order to have a well-established differentiation, in this thesis the deconstruction operations

which have only a material donator worksite are referred to as “deconstructions on the source”.

Construction operations that use deconstructed materials acquired from a used materials supplier

aren’t referred as deconstruction operations because there is no dismantling process in them; but

since they close the reintegration process of deconstructed materials they are included in the

Deconstruction industry’s activities, and therefore referred as “constructions that include

deconstructed materials”. Operations that have both supplying deconstruction materials site and

designated materials reintegration site are referred as “deconstructions from source to destination”.

Temporary construction elements are also considered to be deconstructible elements, although

these considerations are made mainly by their sellers who use the term “Deconstruction” in a

commercial sense on their promoting websites. The montage and dismount of these elements in a

worksite is referred in this thesis as “deconstruction of temporary elements”.

A work which requires the dislocation of an entire construction maintaining its original form is also

considered as a deconstruction of its kind. The fact that in these cases most of the elements of the

previous construction remain with the exact same function as before, and that these elements will

probably be subject to little or no adaptation works make this type of operation seem somewhat as a

“dismantle and rebuild operation”. None the less, the common definition of deconstruction fits almost

perfectly as the description of this sort of operations; therefore these operations are referred in this

document as “dislocation deconstructions”. These works, along with deconstructions of temporary

elements have the characteristic of producing the least amount of non-reusable waste. Deconstruction

operations regarding the retrieval of materials from remodeling works can also be considered, but will

not be studied since no cases were found documenting it.

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3.5.1. Deconstructions on the source

3.5.1.1. Unfinished office buildings

A company named Bioregional Reclaimed worked on a proposal to dismantle two unfinished

office buildings that were erected in 2001 but never completed. The owner of the buildings had two

options, to demolish them and scrap the steel or to dismantle them and sell the steel on for re-use

(Lazarus, 2005).

Figure 9 - Unfinished office buildings (source: (Lazarus, 2005)).

Table 7 - Costs and revenues for demolishing and dismantling options of the unfinished office buildings (source: (Lazarus, 2005)).

Option 1 - Demolish for scrap Option 2 -Dismantle for reuse

Demolition -15000£ Dismantling -55000£

Scrap value +35000£ Shot blasting -34000£

Net value +20000£ Haulage -6000£

Structural certification -3000£

Handling, storage and sales -30000£

Wastage scrap value +10000£

Re-sale value +150000£

Net value +32000£

The predicted timescale for Option 1 was that the worksite would be cleared in 6 weeks while in

Option 2 it would take about 10 weeks for dismantling and 5 weeks for the clearance of stocks. The

accounted risks were very low on Option 1, but on Option 2 were considered the risk of damaging

materials during dismantling and the risk of being unable to resell the materials. The embodied energy

that would be saved in Option 1 was estimated as 5928571MJ. A few more examples like reflecting

practical exercises of deconstruction are given also in (Kernan, 2002).

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3.5.2. Deconstructions from source to destination

3.5.2.1. Barracks building in Fort Ord, California

A barracks building was to be decommissioned in Fort Ord in California. This building had a great

amount of valuable wood and didn’t have much finish materials or adhesives applied.

Figure 10 - Composition of pictures from the decommission and deconstruction of a barracks building in Fort Ord. (source: (Guy, Design for Deconstruction, 2003)).

The procedures consist of:

a) The typical Fort Ord Barracks building, before the beginning of the deconstruction works;

b) Removal of the roof to ground level where it is safer and faster to deconstruct;

c) Separation of the roof into planes;

d) Removal of sheathing from ceiling joists. Working on an elevated position for convenience;

e) Removal of joists with pry bars;

f) Removing studs from sheathing using the Drive-By method;

g) Pneumatic de-nail station using a “Nail Kicker”;

h) Reclaimed old growth lumber, denailed and planed, ready for new construction;

i) The reclaimed wood was reused for the construction of a new ceiling at the Cal State

University Visitors Center, one of the new institutions at the former Fort Ord. Unfortunately no

information could be found about the amounts of recovered materials.

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3.5.2.2. City of Vancouver Materials Testing Lab

In the Old to New Design Guide (Kernan, 2002) various case studies verify the benefits in using

salvaged materials. The City of Vancouver Materials Testing Lab was built on the grounds of some

recently deconstructed warehouse buildings. Their primary focus was to maximize the use of salvaged

materials. Approximately three-quarters of the building's structure and fabric were constructed using

salvaged and recycled materials. The constructions duration was of 9 months and the estimated cost

savings attributed to the use of salvaged materials were of approximately $50,000, although these

savings must be offset against some increased construction management fees and labor costs. A list

of the savaged materials can be consulted in Appendix E.

Figure 11 - Construction timeline for the Vancouver Materials Testing Lab (source: (Kernan, 2002)).

3.5.2.3. Center for Construction and the Environment, Florida

According to (Greer, 2005), in 2000, the Center for Construction and the Environment at the

University of Florida, found that deconstruction reduced the costs by 37 percent when compared to the

conventional demolition of their of six deconstructed wood-frame residences.

3.5.3. Deconstruction of temporary elements

3.5.3.1. Mallforms temporary walls

A very common example of deconstruction is the use of temporary walls. These are

commercialized by many companies, each with its own design. Some are more resistant and have a

more solid “conventional” wall look, while others sacrifice aesthetics to improve adaptability and

reduce complexity of installation. (Mallforms, 2014) claims their walls start saving money for its user

on the moment of the second use.

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Figure 12 - "Mallforms" temporary walls for offices and temporary barricades for shopping centers (source: (Mallforms, 2014)).

3.5.3.2. ENVY Modular Wall Sistems

The company (ENVY Modular Wall Sistems, 2014), who won the U.S. US Environmental

Protection Agency Honors Green Building Challenge of 2009 in the category of Professional Built

Product, uses a model of business where the clients can only rent their walls instead of buying them.

They claim that every 700 sq. ft. (approximately 65m2) of Envy MWS reduces one TON of landfill

debris from conventional temp walls that are torn down and thrown away at the end of a project. Like

Mallforms walls, ENVY walls are designed to be used indoors or outdoors in Casinos, Museums,

Expo/Conventions, Airports, Hotels and Industrial facilities.

Figure 13 - "ENVY Modular Wall Systems” creating a temporary partition and its patented award winning hinge schematics (source: ( (ENVY Modular Wall Sistems, 2014)).

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3.5.4. Dislocation deconstructions

3.5.4.1. Pavilion of Macau, from Lisbon to Loures

A report of the deconstruction of the Pavilion of Macau is made in the doctoral thesis of (Lobato

dos Santos, 2010). The building was originally inserted in the large scale international exhibition Expo

98 and bought afterwards by the City Council of Loures with the purpose of dislocating it to Loures and

serve the objective of becoming a tea house. The building wasn’t originally intended to be

deconstructed, but its characteristics were favorable to this process due to its steel structure and the

fact that it had screwed joints.

Figure 14 - The Pavilion of Macau in use during Expo 98(on the left) and its deconstruction process (on the right) (source: (Lobato dos Santos, 2010)).

The deconstruction process was initiated by a construction company (non-familiarized with

demolitions) and took 4 months. The rebuilding process started about five months after the ending of

the deconstruction, and due to lack of conditioning and deterioration none of the deconstructed

materials besides the structure were reincorporated. The absence of sketches from the original

project, the inefficient system used to identify the deconstructed elements and the fact that some

elements were missing contributed to the elongation of the rebuilding process.

Figure 15 - Rebuilding of the Pavilion of Macau; the reused elements are painted red and the new elements are painted grey (source: (Lobato dos Santos, 2010)).

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About only 14 percent of the 1820 tons from the original buildings weight weren’t sent to landfill

(1390 tons corresponded of reinforced concrete). From the 14 percent in weight of savaged materials

4 percent were recycled and the 10 percent left were reused. The reused materials consisted on the

steel structure (160 tons) and Viroc panels (19 tons), which are cement fiber board panels composed

of a mixture of compressed and dry pine wood particles and cement (VirocNY, 2014). The total

embodied energy saved on this process, assuming that the reincorporated materials still had a full

usage life ahead, was estimated as 2456232MJ.

This case of deconstruction should be viewed as an example of the need to make a detailed plan

previewing various possible scenarios, and that such a plan must be very carefully executed. A

detailed list containing weights, embodied energy per mass and saved embodied energy can be

consulted on Appendix D.

3.5.4.2. Kaisersaal, Berlin

Figure 16 – Kaisersaal in Berlin’s Sony Center, before translocation (source: (Berlin Bildergalerie, 2014)).

After the fall of the Berlin Wall in 1989, the Emperor’s Hall was listed as a historic monument. In

the context of the euphoric mood and the great expectations for Berlin in the early 1990s Sony, the

main investor, decided to translocate the refurbished pompous Emperor’s Hall – together with parts of

the Esplanade’s façade – into their new “Center” (Schalenberg, 2009).

This 75-metre transfer on special rails, carried out in 1996, cost the company about 75 million

Deutschmarks. The hall was separated from its foundations and lifted 2,5m with computer controlled

air cushions.

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Figure 17 - Scheme for the translocation of Kaisersaal, Berlin (source: (Popular Mechanics, 1996)).

After the buildings lift it was set on rails and pushed onto a 75 meter journey, receiving only 1

percent ratio between horizontal and vertical thrusts. Its dimensions are 17,5x13,6x12,0(m), weighting

about 1,800 tons.

Figure 18 - Translocation of Kaisersaal, Berlin (source: (Sony, 2014)).

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3.5.5. Constructions that include deconstructed materials

3.5.5.1. Railway sleepers from the maintenance of the railroad line Marvão-Beirã

Railroads are a type of construction that has a very low tolerance to displacements. Due to the

heavy loads that railroads support they have a special need for maintenance and require frequent

replacement of the sleepers. Old railroads such as the Marvão-Beirã line had sleepers made of high

quality oak that still had very good mechanical characteristics after they no longer in service. These

sleepers auctioned to private entities.

Figure 19 - Deconstructed railway sleepers used as structural elements for a balcony in a private house in Beirã viewed from above and below (source: taken by the author).

One of the buyers of some sleepers made a balcony by installing the sleepers on a steel structure

designed specifically for that purpose. The fact that the sleepers had sustained a full service life on the

tracks meant that they were also treated regularly with very good products.

In total, 44 sleepers with the dimensions of 2,6x0,25x0,15(m) were used in the construction of the

balcony. Using the density of 750kg/m3 a total amount of 3,22 tons of wood was estimated to be used

in this construction, corresponding to 16377MJ of embodied energy.

3.5.5.2. Don Justo’s Cathedral

A former monk and farmer Justo Gallego has been singlehandedly creating a cathedral over the

town of Mejorada del Campo, close to Madrid for the past 50 years. Modeled on St Peter's basilica in

Rome, it stands over 40 meters high, complete with cloisters, crypt and grand domes. The structure

has mostly been built from discarded materials such as broken bricks and tiles for the walls and oil

drums for the columns. Practically all building materials are scavenged or donated by local

construction teams (Atlas Obscura, 2014).

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Figure 20 - Don Justo’s Cathedral (source: (Atlas Obscura, 2014)).

3.5.5.3. Infiniski’s constructions

Infiniski, a high concept architects firm based in Spain have created a niche in reused/recycled

stylish construction that does not compromise on aesthetics. Their designs contain about 85

percent of pre-used materials and are spreading through Europe, Asia and Latin America. There

are no limitations to the usage of used materials, the examples given below se building shipping

containers supplemented with wooden cargo pallets. The pallets in addition to being cheap and

uniquely aesthetic also have the benefit of providing a cooling effect in hot climates (Infiniski,

2014).

Figure 21 – Infinisky’s constructions: on the left the El Tiemblo house and on the right the Manifesto house (source: (Infiniski, 2014)).

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The final products of Infinisky’s constructions are state of the art houses with bioclimatic design

concerns. The houses are graded as superior to the original purpose of their building materials, and so

this building process can be considered as an upcycling process.

3.5.5.4. Slum houses

Slums are a frequently seen example of the incorporation of used materials as an alternative for

reducing costs. The usage of scavenged materials in a slum is very common. Although the houses are

considered of low quality, this characteristic is attributed not only to inferior materials but also to poor

design, low finish details and unqualified labor.

Figure 22 – Slum in the city of Ho Chi Minh, Vietnam (source: (Long, 2014)).

The above image shows the very probable use of scavenged metal sheets, wood panels and

even car tires as construction materials. The fact that the metal sheets contain different amounts of

corrosion from each other and very different shapes and sizes reveals that they have different ages

and were probably collected from different sources. This example illustrates that Deconstruction is

present in society’s various levels of income, and can be resorted to as a luxury (Infiniski’s

constructions) or in this case, as a need.

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3.6. Principles for an optimized deconstruction process

Deconstruction as a process is practiced in a construction before its final demolition and can be

optimized if done taking into account some guidelines provided by field experts. For a building’s

deconstruction operations to achieve maximum performance, there are some key principles that were

synthetized and adapted from the bibliographic review of (Morgan & Stevenson, 2005), (Mark D.

Webster D. T., 2005), and (Bradley Guy, 2002).

Timeline definition

Time is usually a very important factor for building disassembly; make a detailed complete

plan for deconstruction;

Plan ahead for possible non-favorable scenarios;

Resource planning

Resource efficiency is an ecological issue; the rates of use of any material must be

sustainable and aim to maintain diversity in design and supply;

Get to know the deconstruction site; nothing can replace intimate “local knowledge” in relation

to designing for a particular place.

Approaching strategy

Avoid monocultural deconstruction solutions for different sites; each site is unique in terms of

climate and resources;

Be adaptable; if an element doesn’t seem to dismount right don’t try to force it, take a moment

to analyze the element and adapt to the situation;

Apply the concept of “last in first off” (LOFO); a general rule is to dismantle in the opposite

order as the order in which the construction took place;

Always, use of personal protection equipment (PPE);

Use the same tool logic; have preference on using tools that work in the same way as the

original construction tools as possible;

Transportation planning

Avoid excessive transportation of materials;

Labor planning

Try to include laborers who are familiar in deconstructing buildings;

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Economic benefits

Assess the costs and revenues of dismantling and selling the materials and offset them

against the costs demolishing and disposal of the waste as well as the transportation costs in

both cases.

Check if there are any legal advantages or tax benefits; tax benefits may exist depending on

each city’s regulations.

3.7. Variables when choosing Deconstruction

3.7.1. Choosing Deconstruction on constructions

Using deconstructed materials may or may not be a viable option. When facing the choice

between using new construction materials or old reused materials there are various aspects that

should be taken into consideration:

Distance from the new materials supplier vs. deconstruction materials supplying site;

Quality of the used materials and remaining usage life;

Incremented complexity in incorporating used materials vs. conventional complexity of using

new materials;

Tax benefits of using deconstructed materials;

Environmental gain;

In Potential for Reducing the Environmental Impact of Construction Materials (Lazarus, 2005),

depending of the material and its embodied energy, the author states that there is a maximum

distance worth moving for a reclaimed material before the environmental advantage is lost.

Table 8 - Maximum distance worth moving for a reclaimed material before the environmental advantage is lost (source: (Lazarus, 2005)).

Material Distance (km)

Tiles 150

Slate 450

Bricks 375

Aggregates 225

Timber 1500

Steel products 3750

Aluminum products 11250

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In (Mark D. Webster D. T., 2005), to identify buildings that are easy to disassemble and yield

salvageable characteristics it is important to search for:

Transparency - building systems that are visible and easy to identify;

Regularity - building systems and materials that are similar throughout the building and laid

out in regular, repeating patterns;

Simplicity - building systems and interconnections that are simple to understand, with a limited

number of different material types and component sizes;

Limited number of components - it is easier to dismantle structures that are composed of a

smaller number of larger members than a larger number of smaller members. Larger

members tend to resist damage more easily during the deconstruction process and can be

removed more quickly from the structure.

Easily separable materials - materials should be easily separable into reusable components.

Mechanical fasteners are preferable to adhesives. Composite materials are a difficulty unless

the composite assembly has reuse value as an assembly.

3.7.2. Choosing Deconstruction on demolitions

The general aspects to be taken in account when facing the choice to deconstruct or

conventionally demolish a building who has achieved obsolescence are:

Distance to the landfill;

Distance to a deconstructed materials buyer;

Type of waste generated and price per ton of waste charged by the landfill

Condition of the materials that can be removed and obtainable value for deconstructed

materials;

Price of deconstruction specialized labor and conventional demolition labor;

Increased construction duration due to the deconstruction process;

Tax benefits for donation deconstructing materials to Non-profit Deconstruction companies;

According (Mark D. Webster D. T., 2005) in order to identify building types and materials that are

difficult or impossible to deconstruct or have no reuse value if deconstructed it is important to be

aware of the following signs:

Complex Buildings - Buildings where the structural and other systems are difficult to

understand or hidden are challenging to deconstruct;

Non-Standard Components - custom components may have no use in any other buildings.

Imagine trying to reuse the steel framing making up the exterior envelope of the Bilbao

Guggenheim Museum;

Composite Materials - it may not be possible to disassemble certain types of composite

constructions;

Mixed Material Grades - materials that look similar but have different properties have less

value. For example, a building framed using multiple wood species or steel grades yields a

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potentially confusing array of materials that may not be as effectively reused as materials from

a building constructed using a single material grade;

Environmental Hazards - hazardous materials such as asbestos and lead that require special

handling and worker protection;

3.8. Design for Deconstruction

The goal for designing for deconstruction is to make disassembly an alternative the demolition the

end of the buildings useful lives. By doing so, a quantity of used materials and components is

generated that can be reused or recycled, and can therefore be integrated in the next generation of

buildings. The benefits of designing a building for deconstruction today will not be realized until the

useful lives of the buildings designed for deconstruction have expired.

It is often thought that deconstruction is something that has a part only at the end of a buildings

life. But if the building’s design was made taking into account a possible later deconstruction, you’ll

find that there were applied most of the same principles that would be applied for the design of a

building that were to be easily maintained. This is due to the fact that, for both cases, the most durable

elements would logically be the ones which would be less accessible and the least durable elements

or the ones which might need upgrades would stand upfront, such as telecommunications, electrical

and maintenance systems. A building designed for deconstruction has more potential to evolve with

time as materials, fashions, technologies, and uses change.

(Guy, Design for Deconstruction, 2003) defines design for deconstruction as “the design of

buildings to facilitate future change and the eventual dismantlement (in part or whole) for recovery of

systems, components and materials. This design process includes developing the assemblies,

components, materials, construction techniques, and information and management systems to

accomplish this goal. Again, from the bibliographic review of, (Mark D. Webster D. T., 2005), and

(Bradley Guy, 2002) some guidelines were gathered for designing for deconstruction:

Aim to minimize waste by designing elements for maximum diversity of options when reused.

Aim to minimize waste by increasing the number of times a construction element can be re-

used;

Prefabrication maybe cost effective, but don’t forget the external pollution costs associated

with transportation – aim for local prefabrication wherever possible close to the site;

Use regular building systems and materials that are similar throughout the building and laid

out in regular, repeating patterns;

Limit the number of components. It is easier to dismantle structures that are composed of a

smaller number of larger members than a larger number of smaller members. Larger

members tend to resist damage more easily during the deconstruction process and can be

removed more quickly from the structure;

Use building systems and interconnections that are simple to understand, with a limited

number of different material types and component size;

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Materials should be easily separable into reusable components. Mechanical fasteners are

preferable to adhesives. Composite materials are a difficulty unless the composite assembly

has reuse value as an assembly;

Design taking into account the element’s designed life and reason for obsolescence;

According to (Morgan & Stevenson, 2005), a plan for deconstruction should be issued to all

parties at the outset of the contract to ensure a construction process that enables the deconstruction

plan to operate. To achieve success in deconstruction the following tasks numbered below must be

made sure that are undertaken:

1) Statement of strategy for design for deconstruction relating to the building;

Demonstrate the strategy behind the designed re-usable elements and describe best practice

to ensure they are handled in a way which preserves maximum re-usability.

2) List building elements;

Provide an inventory of all materials and components used in the project together with all full

specifications and all warranties, including details of manufacturers.

Describe the design life and/or service life of materials and components.

Identify best options for reuse, reclamation, recycling and waste to energy for all building

element.

3) Provide instructions on how to deconstruct elements;

Provide up-to-date location plans for identifying information on how to deconstruct buildings.

Where necessary add additional information to the “as built” set of drawings to demonstrate

the optimum technique for removal of specific elements.

Describe the equipment required to dismantle the building, the sequential processes involved

and the implications for health and safety as part of the CDM requirements.

Ensure that the plan advises the future demolition contractor on the best means of

categorizing, recording and storing dismantled elements.

4) Distribution of DfD Plan

Revise the plan as necessary and re-issue to all parties at the handover stage, so that there is

maximum awareness of the DfD requirements for the future, including building owner,

architects and builder.

Place copies of the revised Deconstruction Plan with the legal deeds of the building, the

Health and Safety file and the maintenance file.

A key economic benefit of design for deconstruction is the ability for a client to “future proof” their

building, both in terms of maintenance and any necessary upgrading, with minimum disruption and

cost. The wider economic benefits to society include minimizing waste costs at all levels (Morgan &

Stevenson, 2005).

Otto and Wood states that in design for disassembly the critical factors are the number of tasks,

number of tools, and the time or degree of difficulty of the tasks (Kevin Otto, 2001).

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(Guy & Shell, Design for Deconstruction and Materials Reuse, 2003) defines the preferences on

choosing the construction materials when designing for deconstruction. Wood is considered to be a

highly preferable material in design for deconstruction since it a natural material, flexible for both reuse

and recycling, and can be easily connected using interstitial connecting devices such as bolts. Steel is

also a very interesting material for design for deconstruction due to its ability to span large distances

with a small mass of material granted by its high tensile strength, making it a structural material that

can be dismantled and transported with less effort than concrete for instance. Of the other major

materials is concrete, its greatest utility in design for deconstruction is its durability as a structural

material and its ability to be shaped exactly in the way the building designer conceives it. Being very

durable, this material can act as building envelope and accommodate lesser durable building materials

that can be replaced in an easier way due to the design specifically made for them. Concrete is also a

relatively highly recycled material but is not easy to recycle when it is contaminated by other building

components. Unless these components and sub-components have their own inherent value apart from

allowing the concrete components to be recycled, it is not cost-effective to remove them for the

purpose of recycling concrete components, unless mechanical means are used.

An interesting case of design for deconstruction is the TriPOD Plug and Play Housing System.

The TriPOD is a prototype house that introduces the “Plug and Play” concept. It consists in a series of

“pods” connected together allowing functional flexibility to the occupants as their needs change. The

pods are “plugged” into the core to receive electricity and maintain a comfortable environment. The

main core contains the mechanical equipment, the ducts and pipes and serves as a main circulation

space within the house that is capable of accepting multiple pods. The idea behind the design is to

allow the owners to easily adapt the house to their changing needs by adding or subtracting spaces

without changing the structure of the house. When no longer in need for a pod, the owner may sell it

and acquire a new pod with minimal adaption efforts.

Figure 23 - TriPOD Plug and Play Housing System (source: (Tripod Plug and Play Housing System, 2014)).

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The structure of the TriPOD Is entirely steel made, including structural steel beams, pillars, studs,

joists and insulated metal panels. The walls, the roof and the floor and use a light gauge steel system

to support structural insulated panels. About 95 percent of the structural connections are removable

fasteners that are screwed to the steel frames. Their seams are finger joints sealed with butyl sealant

to facilitate future disassembly and reuse without damaging the panels. No insulation between the

steel studs is needed because the structural insulated panels provide all the insulation necessary.

(Tripod Plug and Play Housing System, 2014) claims that the owners of plug-and-play homes will be

able to enjoy different economic benefits, such as a 10-25 percent reduction in utilities bill. The

designers are confident that high energy efficiency design of the TriPOD will pay off at the end. A

detailed cost report for Tripod’s Shell and Structure, Systems and Finish Materials can be consulted in

the Appendixes F, G and H.

3.9. Deconstruction equipment

In a similar was to the Construction industry, the usage of adequate equipment in deconstruction

operations can lead to increased work productivity and better overall results. While it’s preferable to

use in deconstructions the same type of tools that were used in their construction, there are some

construction elements that require specific tools to undo their construction process.

Before the homologation of laws prohibiting the usage of toxic materials in construction there were

various cases of appliance of these materials, being led based paint a common case. Although the

paint is toxic, the material underneath it can be of value, but the costs of transporting the materials to

an industrial site for paint removing may not be worth the gains of the refurbished materials.

John Stephens, while funded by EPA, built a Mobile Lead Based Paint Removal System (Guy,

Design for Deconstruction, 2003), consisting of a trailer that scrapes the paint of wood planks without

allowing for the dust to contaminate the environment. Its chamber is negatively pressured, capturing

all the hazardous planer shavings. This project has undergone extensive testing and has been

certified by the California Air Resources Board.

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Figure 24 - Mobile Lead Based Paint Removal System (source: (Guy, Design for Deconstruction, 2003)).

a) The trailer parked near the removed materials from the construction site;

b) Led paint covered planks slide into the planer on one side of the trailer;

c) Clean old growth wood planks slide out of the other side of the truck;

Another interesting tool for deconstructing is the Nail Kicker (Nail Kicker, 2014). This tool consists

of a pneumatic piston mechanism inside a gun shaped handle that hammers nails from the pinpointed

end or the head. (Nail Kicker, 2014) claims that its tool can drive the head of nails through material up

to ¾ of an inch thick (approximately 1,91cm), and that the increased work productivity can lead to

achieving the payback of the investment in less the 40 work hours.

Figure 25 - Nail Kicker tool (source: (Toolmonger, 2014)).

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3.10. Legislation that supports Deconstruction

In the development of this thesis there was a search made on the legal framework of C&DW.

Although no international laws were found directly obliging the reuse or deconstruction of construction

materials there are some national or local regulations that have empowered the deconstruction

practice. There was a time limitation in this effort due to a difficulty to contact area specialists from the

various local urban departments of the different Town Halls, as well as a linguistic limitation since most

non-international laws are written in its national language.

In the city of Lisbon, the city’s Municipal Master Plan RPDML (in portuguese: Regulamento do

Plano Diretor Municipal de Lisboa) states on the 29th article that “In situations of partial demolition or

total demolition and reconstruction, when considering that there are decorative elements in the

building’s facade or interior which must be preserved, such as masonry, doors, metalwork, tiles and

other decorative elements, a reinstatement project should be made by the entity with the given

competence”. The author tried to contact Lisbon Town Hall’s urban department by phone call in order

to gather more information, but was consecutively left waiting on line for the call to be transferred to

another person that never got to pick up the phone.

In the United States, the Deconstruction industry is currently supported by a law which has no

direct linkage to the practice of deconstruction. Under section 170 of the US Internal Revenue Code,

private individuals, corporations, and unions can to deduct from their IRS a portion of the amount

corresponding to the value of their donations. In order claim the charitable contribution deduction there

are certain criteria that must be met (About Money, 2014):

Donations must be made in the form of cash or property (a pledge or promise to donate is not

deductible until it’s actually paid);

Donations can only be made to a qualified tax-exempt organization;

The donator must be able to itemize (giving to charity is a great tax planning strategy, but it

only works for people who are eligible to itemize their deductions)

The donator must meet record keeping requirements (this includes saving canceled checks,

acknowledgment letters from the charity, and appraisals for donated property)

Tax exempt organizations are need to be recognized under the section 501(c)(3) of the US

Internal Revenue Code. The Deconstruction non-profit companies benefit from this code by issuing

tax-deductible receipts in exchange for donations of used construction materials and furniture. In the

website of a Deconstruction company (The ReBuilding Center, 2014) it is claimed that they will give a

tax-deductible receipt and documentation for all materials salvaged and donated.

In the Netherlands the Dutch Government there is a law passed on the first of April 1997 which

briefly states that “the dumping of reusable building waste is prohibited” (Bart J.H. te Dorsthorst,

2000).This law promotes the use of alternatives to landfill which supports Deconstruction.

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3.11. Chapter remarks

Deconstruction as a process has its perks, especially when compared with its alternatives like

conventional demolition or recycling. For the practice of deconstruction to be a reality companies have

to choose its methods when facing demolition or construction works.

The state of the art regarding Deconstruction is somewhat confuse in its definitions. Also, the fact

that there are various distinct ways to practice deconstruction activities makes it somewhat confuse for

a non-field person. It can be considered a deconstruction practice to remove small dimension

materials from a building such as roof tiles, or it can also be considered a deconstruction practice to

remove an entire partitioned division. Laics are often found confused, giving less credit to

deconstruction than the credit it deserves. In order to have a well-established differentiation between

deconstruction operations in this thesis the operations are referred with specific given terms.

Although the practice of deconstruction isn’t considered as common there is a significant amount

of documented case studies. The risk of not finding a buyer for the deconstructed materials or a

suitable construction to fit them in and the additional costs that may appear due to those accidents

seems to be the capital reason that drives the industry away from investing on Deconstruction. A safer

conventional choice is always available, and the involved entities don’t seem to be adventurous. This

conclusion is also supported by the fact that none of the 72 sent emails was replied with an answer

revealing willingness to contribute with an interview. The industry’s belief in change is so small that the

smallest efforts are considered as a waste of time.

While most available papers sustain the need for development of Deconstruction in a more

commercial way, basing on its strengths and opportunities, this thesis approaches Deconstruction’s

weaknesses and threats too. To conclude this chapter, a SWOT analysis is made on the practice of

Deconstruction’s activities.

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3.11.1. SWOT analysis

3.11.1.1. Strengths

Increased diversion rate of demolition waste from landfills when compared to conventional

demolition;

Potential reuse of building components;

Enhanced environmental protection, both locally and globally;

Preservation of architecture with genuine old materials, while adapting new construction

techniques, obtaining higher efficiency;

Reduction of the volume of C&DW produced and sent to landfill;

Maximum ambient and resources rentabilisation (exploiting materials until its limit);

Reduction of resource extraction;

Reduction of energy consumption associated to the production of new materials;

If there is no destination found for a given deconstructed element, it can always be recycled;

It’s a good tool for training workers in construction trades;

3.11.1.2. Weaknesses

The quantification and evaluation of a deconstruction process is complex and not always

comparable to conventional methods;

Most of the existing buildings have not been designed for dismantling;

Most of the building components have not been designed for disassembly;

Tools for deconstructing existing buildings often do not exist in worksites;

Disposal costs for demolition waste are frequently low;

Dismantling of buildings requires additional time and planning;

Re-certification of used components is not often possible;

Building codes often do not address the reuse of building components;

The economic and environmental benefits are not well-established, and lack incentive;

Labor costs are usually high;

Lack of established supply-demand chains;

Requires an infrastructure of skilled contractors and laborers who are familiar in

deconstructing buildings;

There is a risk of not finding a buyer or not having a suitable construction for the

deconstructed elements, which results in additional unnecessary cost;

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3.11.1.3. Opportunities

The global economy is in need of new cost-saving solutions;

There is a general growing effort to promote sustainability (Global Reporting Initiative,

2010/11);

There are plenty of used construction material stores;

New technologies that provide better communication between entities (platforms) may be

developed in a recent future;

The milestones set to achieve a minimum target of 70 percent (by weight) for preparation for

re-use, recycling and other material recovery of C&DW by 2020 is very demanding, and will

oblige Demolition industry entities to resort to every possible option;

The fact that deconstruction requires a lot of manual labor can absorb the excess of labor from

low peaks of the construction industry;

3.11.1.4. Threats

The Demolition and Construction industries may never react to Deconstruction, and ignore it;

Labor costs may rise beyond the point where deconstructing no longer remains an

economically feasible option;

New technological advances may produce cheaper building materials that could compete with

Deconstruction;

Opens the possibility to the arise of low cost construction companies, that will use

Deconstruction to gain profits, sacrificing quality and giving Deconstruction a negative image;

The Construction investors in may not realize the full economic benefits of designing for

deconstruction;

The stock flow and quality of used building materials may be unpredictable;

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4. Deconstruction Supporting Platform

4.1. Initial considerations

One of the greatest barriers to the development of the Deconstruction industry is the lack of

linkage between demolition works and construction works. There are companies that receive

deconstructed materials and refurbish them into buildable conditions, but there isn’t a very well-

established connection between these used materials suppliers and the building contractors or design

engineers.

Due to the fact that deconstruction operations aren’t very common overall, the income of materials

to the used materials suppliers is proportionally small. The quality of the used materials may also be

unpredictable. In comparison to the constant flow of stock and quality standards that the construction

materials industry can provide it’s natural that the construction companies might prefer new materials

suppliers.

In order to design for deconstruction, the design engineers need to know which materials are

available. Most of the used material stores don’t have or keep an updated online database. Even if the

inventory was kept online and up to date, a building designer or contractor would need to consult the

inventory of numerous used materials suppliers for each building they were to work on, which would

take a significant amount of time.

Deconstructions from source to destination have the reduced effort of not needing to consult used

materials suppliers. But on the other hand, this type of deconstructions would have an added

aggravation from the fact that the built patrimony is heterogeneous and its buildings designs are

complex and weren’t thought for deconstruction. These characteristics make it difficult to find a good

match between a deconstructed materials source worksite and construction that can receive those

materials.

The data involved in the Deconstruction industry is complex, and the system isn’t reacting in an

effective way. Intending to fill this need, this thesis responds by studying the conceptual creation of a

Deconstruction supporting platform.

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4.2. Aims

The conceptualization of the Deconstruction supporting platform was intended ever since the

beginning of the works involved in the creation of this thesis. Its aim is inspire other entities to develop

it into implementation. Due to the character of this thesis and the authors knowledge not being

extended into the areas of computer science or arts, the conceptualization of the Deconstruction

supporting platform isn’t intended to reach the realms of programming or graphic design. If done so

the projected aims for the resulting platform are:

Making it accessible to all Deconstruction markets

Revolutionize the Deconstruction markets; in the way that beepers evolved into cellphones or

letters into emails, the Deconstruction markets will have a much more efficient tool to

communicate;

Help expand the Deconstruction industry; the increased business and will generate an

increased dedication in investigation in this area, which will generate new developments,

increasing business and so on;

Spread out the mentality of reusing materials, giving the example that in the same way

construction waste can be explored to its highest utility many other wastes can be reused too;

4.3. Analysis of the current deconstructed materials market

The web listed deconstructed materials companies follow two overall very similar business

models. There are the regular reused building material companies and the non-profit reused building

material organizations. Both ask the client for information and pictures about the materials and offer a

rough tender free of charge. If there are significant amounts of interesting salvageable materials and

the client is willing to accept the estimated value the deal is closed and the deconstruction process is

started. The non-profit organizations give tax-deductible receipts in the agreed amount in exchange for

the materials while the regular companies pay for them.

Generally, both deconstructed materials types of companies (profiting and non-profit) provide the

labor for extracting the materials with their own teams of experienced deconstruction workers. Some

of the used construction materials companies who have a strong internet presence are listed on Table

9.

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Table 9 - Used construction materials companies (source: author-made research)

Business Model

Designation Link

Non-profit The Reuse People of America http://www.thereusepeople.org/

Non-profit Whole House Building Supply and Salvage http://driftwoodsalvage.com/

Non-profit Construction Junction http://www.constructionjunction.org/

Non-profit The ReBuilding Center http://rebuildingcenter.org/

Non-profit Building Resources http://www.buildingresources.org/

Non-profit Habitat for Humanity http://www.habitatgsf.org/

Non-profit Rebuilding Together Peninsula http://www.rebuildingtogetherpeninsula.org/

Non-profit Rebuild Warehouse http://rebuildwarehouse.org/

Profiting American Iron and Lumber Inc. http://www.americanironandlumber.com/

Profiting Omega Salvage http://www.ohmegasalvage.com/

Profiting Crossroads Recycled Lumber http://crossroadslumber.com/

4.4. Target

When fully implemented the platform is intended to have a worldwide international reach. Given

the circumstance that most of the countries don’t have yet a defined used materials market with

sellers, buyers and deconstruction experienced workers, the platform is initially targeted at a smaller

range of users. This range is set to target only the communities who combine all the three agents

mentioned above, such as the USA market.

4.5. Concept of the platform

The platform is intended to link entities involved in demolitions, constructions, and middle entities

as the deconstructed materials companies. Demolition involved entities are demolition companies,

owners of constructions who are planned to be demolished, or anyone who may be entitled to

ownership of the materials from a building. Construction involved entities can be contractors, building

designers, architects, or construction investors. Deconstructed materials companies are used

materials suppliers, used materials refurbishment companies, and any entity that may be interested in

acquiring used construction materials for storage, refurbishing and resale. Between these three

entities there are three possible connections.

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Figure 26 - Links between the entities involved in Deconstruction (source: created by the author).

On the first connection the user makes with the platform, he is greeted and asked which the three

categories of users does he fit in. The access can only be granted though registration, verification and

login.

Once validated, demolition involved entities will be able to publish the materials or building

elements that they see as valuable assets. These publications are accessible to all users.

Deconstructed materials companies will also be able to publish the materials or elements they have in

storage, being these publications of access to all users. Construction involved entities only have the

need to access published information, therefore they cannot publish.

4.6. Login, registration and verification of the entities

All entities have to fill out a registration form according to their category. A copy of the company’s

license is requested for verification (if possible) and the data is confirmed through the data provided

by the Institute of Construction and Real Estate – INCI (in portuguese: Instituto da Construção e do

Imobiliário), which has a complete up to date list of data on licensed construction and demolition

entities. This is the preferable verification process. The possibility of establishing partnership with INCI

is highly valued and may be a mean to automate the process.

The companies that can’t be verified by the above process are requested to send a copy of the

owner’s citizen card through a company’s email, this e-mail must be an e-mail that is offered as a

contact on the company’s website.

All entities have to accept a Disclaimer agreement stating that they accept all the responsibilities

associated to their publications, and that the platform cannot be in any way responsible for harm done

to users through the platform.

Login is made possible after the verification of the entities through insertion of user name and

password.

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Figure 27 - Diagram of the connections between the Decontruction supporting platform's clients and the platform itself (source: created by the author).

4.7. Security

In order to protect the platform from automated cyber-attacks the registration procedure includes

a security step, in which the user has to write a word generated by a random algorithm. Every failed

attempt to login after the second try will also need to pass through this security step. After the tenth

consecutive failed login attempt, an alert system is activated that results in blocking the IP used for

those login attempts is blocked for the next hour and simultaneously a notification is sent to the

blocked user by e-mail informing of the occurrence.

4.8. Publishing on the platform

For a user to publish a construction material or element that he’s selling on the platform a

“construction material/element publishing form” must be filled online containing the following fields:

Type – the user has two lists available, one for construction materials in which are listed the

various categories of construction wastes in the European List of Wastes, and another list for

construction elements that consists of the various deconstructible elements (door, window,

solar panel, false ceiling structure, moveable wall, others);

Function – there are several checkboxes the user can select such as “structural”, “non-

structural”, “exterior”, “interior”. The user should only select the checkboxes to which the

material may fit the purpose;

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Quantity – consists in filling two fields being “amount” and “unit”, in which the “amount” field is

filled with a numeric value and the “unit” field is a selection on the most frequently

internationally used unit systems (kg, ton, lb., m, m2, m3, in., sq.in., cu.in.);

Condition – the user selects the condition that best describes the material he’s selling from a

list of five possible conditions (excellent, very good, good, medium and poor);

Description – the user states in a textbox all the characteristics of the material/element that

couldn’t be described above such as section dimensions, defects, color or materials (in case

of the construction elements);

Requires dismantling? – the user is prompted if the materials are already dismantled or

require dismantling works by simple selection of one of two checkboxes, “yes” or “no”; in case

of an affirmative answer the field “Availability” appears bellow;

Availability (only visible if the field “Requires dismantling?” is answered “yes”) – consists in

filling two fields being “From” and “To”, in which the user selects two dates;

Location (of the materials) –the preferred method is pinpointing on an available map (Google

maps or Bing maps are two possibilities); another possibility is submitting an address that will

automatically be converted into coordinates;

Submit pictures – an upload link is available to submit pictures;

An example of this form is illustrated in Figure 28.

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Figure 28 - Construction material/element publishing form (source: created by the author).

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4.9. The database

As a result of the submission of multiple publishing forms the database starts to have a wide

variety of materials/elements to be consulted. It’s now possible for the potential buyers to start

searching the platform for their needs. An example of the Deconstruction platform’s database in a raw

format can be analyzed in Table 10.

Consulting the database is a process somewhat inverse to inserting forms into it. To do so, a

“search form” must be filled containing these fields:

Type and Function – both these fields are filled in the same way as the homonymous fields in

the “construction material/element publishing forms”;

Condition – the five possible conditions (excellent, very good, good, medium and poor) are

shown as check boxes, the buyer can select any of the five;

Requires dismantling? – in the search form this field is renamed to “Are you willing to

dismantle?”; two “yes” or “no” check boxes are available as before; if the answer is “yes” the

same “Availability” field appears bellow;

Availability (only visible if the field “Are you willing to dismantle?” is answered “yes”) – consists

in filling two fields being “From” and “To”, in which the buyer selects two dates that will

afterwards crossed with the sellers availabilities;

Location (of the materials) –the user is prompted what is his location by pinpointing it on a

map and how far is he willing to travel by filling a numeric box;

Quantity” is not being included in the search fields because it tends to narrow the choices too

much. If at a given stage of the platform’s evolution is noticed that the search results are too wide the

“quantity” may be used then;

The search engine then analyzes and crosses the available data with the requests made and

shows as results the information of the materials that fit the description. Information like “quantity”,

“description” and the submitted pictures are now available. The sellers contact is shown too.

Note: the less the user fills the search form the more results are shown.

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Type Function

Availability Location

User Constr. Materials

Constr. Elements

Str. Non-str.

Int. Ext. Quant. Unit Condition Req.

From To Coordinates Address Description Annexes dism.

DMC1 wood - yes yes yes yes 20 - Excellent no - - 370.777.991,00

9x9x150(cm) oak joists Picture1 -801.778.745

DMC2 glass - no yes yes yes 3 - Excellent no - - 372.880.057,00 120x100x0,3(cm)

laminated transparent glass

Picture2 -812.466.383

DIE1 - windows no yes no yes 6 - Good yes 05-10-2014 05-12-2014 366.588.695,00 Antique Victorian window

frames with vitrals; dimensions 120x60(cm)

Img08 -766.955.203

DIE3 - doors no yes yes no 22 - Very Good yes 11-08-2014 11-10-2014 34.371.608,00 15060 U.S. 17,

Hampstead, NC 28443, USA

Office wooden doors with frames and hardware; dark natural wood colored

Picture3 -77.705.465

DMC1 insulation materials

- no yes yes yes 150 m2 Excellent no - - 370.777.991,00

Mineral wool 8cm thick Img00 -801.778.745

DMC1 tiles - no yes no yes 400 - Medium no - - 370.777.991,00

Orange standard roof tiles Picture -801.778.745

DIE2 - cooper wire

no yes yes yes 800 m Very Good yes 30-07-2014 30-09-2014 34.371.608,00 15060 U.S. 17,

Hampstead, NC 28443, USA

Acquired to power a music festival; company went bankrupt

Cooper cables.jpg -77.705.465

DIE4 wood - no yes yes yes 40 - Medium yes 14-08-2014 14-10-2014

34.003.799,00

1601 Gervais St, Columbia, SC 29201, USA

Flooring pine wood boards measuring 300x20x1(cm), varnished used for 10 years. About 10% may be unusable due to an infiltration that occurred last year.

Picture5 -81.026.628

DIE1 - photo voltaic panels

no yes no yes 10 m2 Very Good yes 05-10-2014 05-12-2014 366.588.695,00 Two modules of 2x2,5(m)

roof solar panels -

-766.955.203

DMC2 - others no yes yes yes 1 - Good no - - 372.880.057,00 Mitsubishi Mini-Split HVAC

System img01

-812.466.383

Table 10 - Example of the Deconstruction platform’s raw database after the publication of eleven material/element forms; DMC stands for Deconstruction Materials Company and DIE stands for Demolition Involved Entity (source: author).

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4.10. Revenues and costs

Revenues are planned to be made from sponsorships and electronic ads. There are various

companies that work in the electronic adds marked, being Google Ads well conceited choice.

Sponsorships have to be searched for; in the initial phase a search on competitions for startup

businesses is highly recommended.

An alternative source of revenues would be charging the users a fee. In this case, only the sellers

should be charged. This fee could be charged by sale as a small percentage, as a periodical fee or a

mixed concept in which depending on the volume of sales of a given user he would belong in a certain

category and pay the that category’s corresponding fee periodically.

Besides the initial investment in equipment, the costs which the platform will also have to support

are the hosting server rent, the domain registry rent, staff salaries, facilities, taxes and bills.

4.11. Chapter remarks

Construction has a tradition of being one step behind in technology. Composite fiber components

were applied in other industries far before they appeared in construction. Nanotechnology has been

talked about for a few years and isn’t yet applied in normal constructions. Tradition seems to be the

obstacle. The same principles of deconstruction are applied every day in other businesses like the

automobile sector, where cars are designed to be easily disassembled for both maintenance and end

of life, and dismantled to parts that are mostly sold as used replacement parts or recycled.

Although the original aim of creating the concept of a Deconstruction supporting platform was

completed, the fact that it meant to achieve a concept without having it undergo implementation leaves

somehow a sensation of incompleteness. The full creation and implementation of this platform is

undoubtedly a proposed future work.

One characteristic that makes this project interesting for a developer is that it doesn’t need a

heavy investment to start up. The capital at risk is significantly low in comparison to the possible

winnings in connecting together large cash flow markets such as those in the Construction industry,

the Demolition industry and the Deconstruction related entities.

It is now up to involved agents of Construction to adopt or ignore the use of new information

technologies, the author certainly recommends it.

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5. Future Developments and Conclusions

5.1. Future Developments

The works that in this thesis are considered as “works of deconstruction” or “deconstruction

related works” have very distinct characteristics. Deconstruction may apply to recovering materials

from a building that is going to be demolished or, sometimes, apply to the total dislocation of a

building. The definitions of the different deconstruction works haven’t yet been differentiated. A future

development is suggested on defining the works of deconstruction individually, with emphasis on their

characteristics and limitations.

In the legal framework review of C&DW it was noticed that the legal system can be better adapted

to the practice of deconstruction. The distinction between reusing or recycling C&DW isn’t yet legally

made. With no laws promoting the activity of deconstructing and with a Recycling industry in a stage of

development years ahead the Deconstruction industry probably won’t be able to grow to its full

potential anytime soon. A work is proposed on analyzing the legal system and studying the possibility

of legally separating these two different ways of C&DW treatment.

This study presents the conceptualization of a Deconstruction supporting platform targeted at the

entities involved in construction, deconstruction and demolition worldwide. It is a concept that, if well

implemented, can create a network between the above mentioned entities that will result in

foreseeable increase of resource efficiency. With the collaboration from these entities and their

associations with a research institute a much deeper knowledge of the needs of the Deconstruction

industry can be obtained and applied in the development of the Deconstruction supporting platform.

This development can obtain its maximum results when combined with a professional team of web

designers and programmers. For a future work it is proposed the full creation, development and

implementation of the Deconstruction supporting platform.

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5.2. Conclusions

Sustainability in Construction has now a well-established set of tools; more so, the constant

change in the world’s mindset seems to be in the direction of sustainable development. The need of

recognizing a building’s sustainability and its materials Lifecycle environmental burden are now valued

measures that have become of interest to the private sector.

Deconstruction is one of Sustainability’s tools. It is present in today’s society various levels of

income, and is resorted to both as a luxury and as a need. Its related practices have existed probably

ever since mankind stopped being nomadic. There are documented cases of deconstructions starting

on the medieval period, and although not evolving much until a recent past they now seem to be

gradually emerging as an alternative to conventional demolition.

One of the obstacles preventing Deconstruction to succeed is the lack of legal support, since

there are no laws that promote deconstruction alone. Legally, the integration of reused materials on a

construction is equivalent to the integration of recycled materials. Being the Recycling industry a much

more developed industry than Deconstruction, the choice to incorporate recycled materials is naturally

preferred by construction companies rather than incorporating deconstructed materials. However, to

build cheaper but in a less sustainable way or to invest more in constructions that will be adaptable to

new needs while demanding less from the environment is less of a paradigm every time

Deconstruction reaches a new development.

The possible investors in Deconstruction may still be driven away by the risk of not finding a buyer

for the deconstructed materials or a suitable construction to fit them in. The additional costs that can

result from not finding a materials donator/receiver compatible pair seems to be the capital reason that

drives the industry away from investing on Deconstruction. But as the industry of Deconstruction

grows this difficulty loses its weight, for a snowball effect is to take over and there will be more and

more offer and demand for used construction materials.

The milestones set for 2020 will surely pressure the C&DW generating industries to change their

operating methods, possibly opening new doors for Deconstruction. The oncoming opportunity for

Deconstruction needs to be complemented with a change in the conventional mindset of the

Construction and Demolition industries. New construction building designs and building demolitions

need to be thought taking into consideration the possibilities that Deconstruction provides.

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Appendixes

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Appendix A - Prices charged for incoming materials at TRIANOVO recycling plant (source: (Trianovo, 2014)).

Tipologia Densidade Preço unitário

(ton /m 3) (€/ton)

RCD sujos 0,17 160,00 €

RCD sujos 0,2 130,00 €

RCD sujos 0,25 100,00 €

RCD sujos 0,3 80,00 €

RCD sujos 0,35 68,00 €

RCD sujos 0,4 59,00 €

RCD sujos 0,45 52,00 €

RCD sujos 0,5 46,00 €

RCD sujos 0,55 41,00 €

RCD sujos 0,6 37,00 €

RCD sujos 0,65 34,00 €

RCD sujos 0,7 31,00 €

RCD sujos 0,95 22,00 €

RCD sujos 1,1 15,00 €

RCD sujos 1,25 7,50 €

RCD limpos 1,25 5,50 €

Terras Limpas - 2,00 €

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Appendix B - Sector 17 of the European List of Wastes, regarding C&DW. Any waste marked with an asterisk (*) is considered as a hazardous waste pursuant to Directive 91/689/EEC (source: (European Commission, 2000)).

17 CONSTRUCTION AND DEMOLITION WASTES (INCLUDING EXCAVATED SOIL FROM CONTAMINATED SITES)

17 01 concrete, bricks, tiles and ceramics

17 01 01 concrete

17 01 02 bricks

17 01 03 tiles and ceramics

17 01 06* mixtures of, or separate fractions of concrete, bricks, tiles and ceramics containing dangerous substances

17 01 07 mixtures of concrete, bricks, tiles and ceramics other than those mentioned in 17 01 06

17 02 wood, glass and plastic

17 02 01 wood

17 02 02 glass

17 02 03 plastic

17 02 04* glass, plastic and wood containing or contaminated with dangerous substances

17 03 bituminous mixtures, coal tar and tarred products

17 03 01* bituminous mixtures containing coal tar

17 03 02 bituminous mixtures other than those mentioned in 17 03 01

17 03 03* coal tar and tarred products

17 04 metals (including their alloys)

17 04 01 copper, bronze, brass

17 04 02 aluminum

17 04 03 lead

17 04 04 zinc

17 04 05 iron and steel

17 04 06 tin

17 04 07 mixed metals

17 04 09* metal waste contaminated with dangerous substances

17 04 10* cables containing oil, coal tar and other dangerous substances

17 04 11 cables other than those mentioned in 17 04 10

17 05 soil (including excavated soil from contaminated sites), stones and dredging spoil

17 05 03* soil and stones containing dangerous substances

17 05 04 soil and stones other than those mentioned in 17 05 03

17 05 05* dredging spoil containing dangerous substances

17 05 06 dredging spoil other than those mentioned in 17 05 05

17 05 07* track ballast containing dangerous substances

17 05 08 track ballast other than those mentioned in 17 05 07

17 06 insulation materials and asbestos-containing construction materials

17 06 01* insulation materials containing asbestos

17 06 03* other insulation materials consisting of or containing dangerous substances

17 06 04 insulation materials other than those mentioned in 17 06 01 and 17 06 03

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17 06 05* construction materials containing asbestos

17 08 gypsum-based construction material

17 08 01* gypsum-based construction materials contaminated with dangerous substances

17 08 02 gypsum-based construction materials other than those mentioned in 17 08 01

17 09 other construction and demolition wastes

17 09 01* construction and demolition wastes containing mercury

17 09 02* construction and demolition wastes containing PCB (for example PCB-containing sealants, PCB-containing resin-based floorings, PCB-containing sealed glazing units, PCB-containing capacitors)

17 09 03* other construction and demolition wastes (including mixed wastes) containing dangerous substances

17 09 04 mixed construction and demolition wastes other than those mentioned in 17 09 01, 17 09 02 and 17 09 03

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Appendix C - Lifecycle Assessment Software and Databases (source: various documents and

author-made research).

Designation Link

Athena Institute http://www.athenasmi.ca/

Building for Environmental & Economic Sustainability (BEES)

http://www.bfrl.nist.gov/oae/software/bees/

Building Life-Cycle Cost (BLCC) http://www1.eere.energy.gov/femp/information/download_blcc.html

CMLCA http://www.leidenuniv.nl/interfac/cml/ssp/software/cmlca/index.html

ECOEFFECT http://www.ecoeffect.se

Eco-Indicator 99 http://www.pre.nl/eco-indicator99/default.htm

ECO-it 1.3 http://www.pre.nl/eco-it/default.htm

Economic Input-Output Life Cycle Assessment (EIOLCA)

http://www.eiolca.net/

EcoScan 3.0 http://www.tno.nl/

EQUER http://www.izuba.fr

EPS 2000 Design System http://eps.esa.chalmers.se/

GaBi 4 Software System and Databases

http://www.gabi-software.com/

GEMIS (Global Emission Model for Integrated Systems)

http://www.oeko.de/service/gemis/

GREET Model http://www.transportation.anl.gov/modeling_simulation/GREET/index.html

GREENCALC http://www.greencalc.com

IDEMAT http://www.idemat.nl/

IVAM LCA Data 4.0 http://www.ivam.uva.nl/index.php?id=74&L=1

LCAiT 4 http://www.lcait.com/main_index.html

LCAPIX http://www.kmlmtd.com/index.html

MIET 3.0 - Missing Inventory Estimation Tool

http://www.leidenuniv.nl/cml/ssp/software/miet/index.html

OpenLCA http://www.openlca.org/index.html

REGIS http://www.sinum.com/htdocs/e_software_regis.shtml

SimaPro Life Cycle Assessment Software

http://www.pre.nl/simapro/inventory_databases.htm

SPINE@CPM http://www.cpm.chalmers.se/CPMDatabase/AboutDatabase.htm

SPOLD Data Exchange Software http://lca-net.com/spold/

TEAM™ http://www.ecobilan.com/uk_team.php

The Association of Plastics Manufacturers in Europe (APME)

http://www.plasticseurope.org/

The Boustead Model 5.0 http://www.boustead-consulting.co.uk/products.htm

The ecoinvent Centre http://www.ecoinvent.com/

U.S. Life Cycle Inventory Database http://www.nrel.gov/lci/

Umberto - Life Cycle Assessment Software

http://www.umberto.de/en/index.htm

WISARD™ http://www.ecobalance.com/uk_wisard.php

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Appendix D - Average embodied energy in construction materials (source: (Andrew Alcorn, 1998)).

Material Embodied energy

MJ/kg MJ/m

Calcium carbonate 1.3

Cellulose pulp 14.3

Cement, average 9.0 17550

Cement, dry process 7.7 15020

Cement, wet process 10.4 20280

Cement grout 1.9 4560

Cement mortar 2.1 3360

Fibre cement board 10.9 15550

Soil-cement 0.7 1420

Ceramic

Brick, old technology 7.7 1580

Pipe 6.8 13880

Refractory brick 5.7 12830

Concrete

Block-fill 1.4 3150

Block-fill, pump mix 1.5 3430

Grout 1.7 2380

17.5MPa pump mix 1.2 2830

Earth, raw

Adobe, straw stabilised 0.22 360

Adobe, cement stabilised 0.67 1130

Clay 0.07 45

Clay for cement 0.1 65

Rammed soil cement 0.73 1450

Insulation

Wool (recycled) 20.9 200

Paper

Kraft 13.9

Plaster, gypsum 3.8 5480

Stainless steel, average 50.4 395640

Steel, imported, structural 35.9 281820

Timber

Kiln dried, average, dressed 5.09 2200

Kiln dried, gas fired, dressed 8.2 3550

Kiln dried, waste fired, dressed 3.1 1340

Water, reticulated 0.003 3.3

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Appendix E - Savaged materials from the Vancouver Materials Testing Lab (source: (Kernan, 2002)).

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Appendix F- Detailed cost report for TriPOD’s Shell and Structure (source: (Tripod Plug and Play Housing System, 2014)).

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Appendix G - Detailed cost report for TriPOD’s Systems (source: (Tripod Plug and Play Housing System, 2014)).

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Appendix H - Detailed cost report for TriPOD’s finish materials (source: (Tripod Plug and Play Housing System, 2014)).

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Appendix I - Mass, embodied energy, and specific embodied energy of the materials that composed the Macau Pavilion at Expo 98 (source: (Lobato dos Santos, 2010)).

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Exmo. engenheiro «prefixo» «Nome_da_empresa»,

Sou estudante do IST, estou a realizar uma tese de mestrado com o tema de "Desconstrução no

ciclo de vida das construções" e procuro saber em que medida é que a «Nome_da_empresa»

emprega técnicas associadas à desconstrução nas obras que realiza.

Quando menciono desconstrução, refiro-me à desmontagem de materiais de uma obra

previamente à sua demolição/desativação para que estes venham a ser reincorporados em

construções futuras sem passarem por reciclagem ou ser levados a aterro, contribuindo para a

redução de custos de obtenção de novos materiais e de emissão de resíduos. No ciclo de vida das

construções entende-se que, quando uma obra excede a sua vida útil nem todos os seus materiais

constituintes estão necessariamente obsoletos. Uma parte dos materiais constituintes da obra deve

ter uma vida útil remanescente considerável, podendo muitas vezes ser desmontados e

reincorporados numa nova obra sofrendo apenas pequenos ajustes de dimensão e tratamentos,

quando necessário.

Um dos objetivos da minha dissertação é a criação do conceito de uma plataforma que faça a

ligação entre obras a demolir e obras a construir, e os materiais que podem transitar de uma obra

diretamente para a outra sem terem de passar por processamentos dispendiosos, ou envio para

aterro.

O que pretendo é conhecer quais as técnicas que se praticam atualmente que tenham o objetivo

de não desperdiçar bons materiais de construção pertencentes a uma obra que por algum motivo

teve o fim da sua vida útil declarado. Esta informação não se consegue obter por consulta de artigos

ou bibliografia, é um conhecimento que está apenas na experiência das pessoas que praticam

engenharia civil, e como tal gostaria de saber se a «Nome_da_empresa» tem disponibilidade para me

receber numa reunião num futuro próximo, ou se por via email ou chamada telefónica pode transmitir-

me o conhecimento que tem nesta área.

Será feita referência na tese das empresas que contribuíram para a criação do conceito da

plataforma de apoio à Descontrução.

Os meus agradecimentos,

Manuel Catarino - 919247480

Appendix J - Template of the email that was sent to 72 different portuguese construction industry and deconstruction related companies.


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