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Article

Getting Environmental Information from Construction Cost Databases: Applications in Brazilian Courses and Environmental Assessment

by
Luis Claudio A. Borja
1,2,*,
Sandro Fábio César
3,
Rita Dione A. Cunha
3 and
Asher Kiperstok
2
1
Federal Institute of Bahia (IFBA), BR 324-km 102.11, S/N-Aviário, 44135-000 Feira de Santana, Brazil
2
Post-Graduate Program in Industrial Engineering (PEI), Federal University of Bahia (UFBA), Aristides Novis, 02, Federação, 40210-630 Salvador, Brazil
3
Post-Graduate Program in Civil Engineering (PPEC), Federal University of Bahia (UFBA), Aristides Novis, 02, Federação, 40210-630 Salvador, Brazil
*
Author to whom correspondence should be addressed.
Sustainability 2019, 11(1), 187; https://doi.org/10.3390/su11010187
Submission received: 30 November 2018 / Revised: 20 December 2018 / Accepted: 20 December 2018 / Published: 1 January 2019
(This article belongs to the Section Environmental Sustainability and Applications)

Abstract

:
The traditional decision-making process in construction is still driven by factors such as cost and time, not adequately addressing indicators to control their environmental impacts. So, how to improve environmental communication to incorporate sustainable building practices. The incorporation of environmental indicators may enlarge the scope of construction management tools. In the case of cost databases, widely used in the construction sector, this action can contribute to the communication and dissemination of environmental practices. This paper mapped 24 indicators from construction cost databases to assess their ability to communicate and disseminate environmental information. The research comprised: (a) a review of the use of cost bases in the environmental study, (b) identification of the most cited bases in 27 Brazilian civil engineering courses, and (c) analysis of the selected databases through of the assessment matrix, it crosses cost data versus environmental information. CYPE, TCPO, and ORSE presented performance medium, and higher results than SINAPI, BDCCM, and BCCA. The tools presented low control over environmental information, such as water and energy consumption, machine circulation and pollution generation. However, it has been observed that when adding environmental indicators, these tools can contribute significantly to disseminate good practices in its wide user base.

1. Introduction

The definition and implementation of actions in the search for more sustainable urban systems and constructions are directed by social, economic and financial, institutional, technological, personnel involved, knowledge and innovation, all taking into account the local context and its complexities [1]. Economic and financial factors include costs during the life cycle. In this sense, the challenge is to combine the lowest environmental impact with the cost-optimal during the life cycle [2], reducing the construction process externalities [1].
Initially, life-cycle costs (LCC) emerged to support the project economic choice. In general, such analysis begins with the identification of the constructive activities involved, followed by identification and measurement of their inputs and outputs in terms of time and cost for acquiring materials and services. In recent decades, with the consolidation of the concept of sustainability (balance among the economic, environmental and social dimensions), the need to harmonize economic costs and socio-environmental impacts has increased. Thus, the LCC began to seek to reconcile the economic dimension with the environmental dimension in the choice of low-impact products and processes [3]. Similarly, economic costs have also been incorporated into certification and environmental assessment systems, such as Leadership in Energy and Environmental Design (LEED), British Building Research Establishment Environmental Assessment Method (BREEAM), and Comprehensive Assessment System for Building Environmental Efficiency (CASBEE) [4,5,6]. In the environmental literature, this integration involves the optimization of economic costs and environmental costs, for example, the reduction of resource consumption and waste generation [7], use energy efficiency [8] and reduction of pollutant emissions [9].
In this sense, an economic tool such as LCC can work in conjunction with environmental analysis methodologies during the construction life-cycle. Applications for LCC can be observed in Life-cycle assessment (LCA) [10,11], Life-cycle carbon emissions (LCCE) [12], Life-cycle energy analysis (LCEA) [13]. However, combined analysis of LCC, LCA, and LCCE presents challenges, which require time and research to address the different environmental, economic and social requirements. In addition, new approaches have emerged which correlate economic costs and environmental impacts to project management and construction practices, through the adoption of technologies such as BIM [12,14,15] and methodologies such as Lean Construction [16].
The choice of the evaluation model traditionally also has an impact on the profile of the data to be adopted. Thus, the use of quantitative data predominates in construction cost evaluation systems [17,18,19], on the other hand, most environmental assessment instruments have been adopting a qualitative approach [20,21]. In fact, budgets and cost systems are based on quantitative metrics (e.g., quantities of resources consumed, volumes of waste generated, time spent on activity) [22,23,24], beyond others project data and of their bill of quantities (BOQ) [25,26]. Meanwhile, environmental and sustainability systems often choose subjective criteria (e.g., expert assessment, scales of comparison) for selecting and excluding the indicators, their weights, and aggregation models, it toward to equate the different dimensions of sustainability (social, environmental and economic) [10,21].
In recent decades, new methodologies and systems have been proposed to reduce the subjectivity in the predictive models of the environmental impacts generated by the constructions. Chen et al., (2000) established a construction pollution index (CPI) to estimate the magnitude of the impacts in relation to the duration of construction activities foreseen in the construction schedule [27]. Gangolells et al., (2014) used data from the list of global enterprise quantities in the definition of a scale of weights to predict and compare environmental impacts [21,28]. In both systems, the quantitative data aim to increase the reliability of these models for supporting the decision process and evaluating the available constructive solutions and compare projects.
However, the large volume of data and concepts in multiple areas of knowledge may make it difficult to define the criteria for assessing and measuring the weights of each aspect [29]. A tool to address this issue are the so-called Decision support systems (DSS) [30]. The use of DSS, driven by computational advances, has grown in recent years, allowing their users to aggregate and analyze a large volume of data and information [29]. These analyses have been improving the evaluation and decision-making models for more environmentally-friendly products and processes. Applications of DDS in environmental management can be observed in applications that are related to urban development [29,31], occupational health and safety [32], construction waste management [33,34], and Geographic Information System (GIS) [35]. According to Kazak and Hoof [29], The DDS tools development should consider 3 keys aspects: (a) the ability to quantify features to reduce subjectivity and increase reliability; (b) the size of the potential results, according to the intended objective, ranging from the comparison within a finite set of choices to the use of open list to test solutions through an interactive process; and (c) the degree of uncertainty, considering the changes between the initial conditions and the implementation process.
In summary, the integration between cost bases and environmental performance assessment models can support to improve both tools in the decision-making process. Quantitative data from the cost bases reduce the subjectivity of environmental tools. At the same time, environmental indicators broaden the scope of the databases by adding sustainability criteria in the description of activities and allowing a comparison beyond the economic dimension in the choice and planning of activities.
Additionally, cost bases are widely used in construction practice, many of which are mandatory. The statistical data on consumption and productivity of these bases undergoes constant revision of the maintainer institution, including data collection directly from the productive sector. The cost bases are also present in most of the curricular content of courses such as civil engineering, production engineering, and architecture. Therefore, such a cost base can be a vehicle to disseminate environmental knowledge among construction workers and construction professionals.
In this context, the article carried out a mapping of environmental indicators in databases of costs to assess their ability to communicate and disseminate environmental information, and use in environmental control systems.

2. Materials and Methods

Figure 1 shows the workflow adopted in the research comprising three steps. The first step has mapped an overview of the applications of cost databases in the state of the art of environmental research and the state of the art of construction management. The second stage has implemented a matrix of assessment of the environmental communication on the cost databases. The final step has classified and analyzed the results, comparing the performance of each tool.
The analysis of the use of construction cost databases in environmental research have adopted a systematic literature review (RSL) of articles. The RSL classified and analyzed these articles by theme approached, research region, environmental tools used, the database of costs cited and what the application of these bases in the environmental study.
The survey of the Brazilian cost databases carried out a documental analysis in pedagogical projects of the engineering courses (PPC) and their programs, which were obtained in the electronic sites of the courses as described in Appendix A (Table A1). The search criterion was the occurrence of the following terms: cost database, construction costs or unit cost compositions. The data collection selected a sample of civil engineering course for each Brazilian state and the federal district, with the preference for courses in federal universities.
The selection of cost databases combined the results of the review of the state of the art and recognition of the construction sector [36]. The analysis of the literature has resulted in the selection of the international databases. In the selection of the national databases, the number of citations in the course projects analyzed prevailed.
An Environmental Communication Assessment Matrix (ECAM) was created to evaluate the cost databases performance (Table 1). The ECAM structure has intended to correlate the identified cost data with the degree of detail of the associated information. The variables were grouped into 5 themes: IC, information and communication; RW, resources consumption and waste generation; PS, public services demand; MP, machines demand and pollution generation; and, HS, occupational health and safety. The selection of these themes considered relevant environmental aspects from international regulations such as the Eco-Management and Audit Scheme (EMAS) [37] and scientific articles related to the evaluation of environmental aspects in construction [21,27,38].
A scale of weights (w) was defined to characterize the information quality of a cost data, varying from 0 to 2 according to the information can contribute to a better perception of the relation between the cost data and the environmental aspect: 0, no information or low quality; 1, partial information; and 2, wide information.
The values assigned to the indicators were added to each of the 5 themes. Therefore, the overall score of each of the 5 themes S (S1, S2, S3, S4, and S5) was obtained by the following expression:
S i = k = 1 n w k
where Si represents the value of environmental theme performance by each selected cost databases with the index i ranging from 1 to 5 (5 themes); w is the value adopted to characterize the quality of the environmental information of the data available from the cost databases with the index k ranging according to the numbers of indicators by theme.
To compare the performance among the different analyzed cost bases, the values given by Equation (1) were normalized, obtaining the normalized scores for the 5 themes (S1, S2, S3, S4, and S5) according to the following equation:
s i = S i S i ,   m a x
Finally, the overall value (G) of the performance of each cost databases was obtained by summing the normalized values (Si) for the 5 themes according to the following equation:
G = i = 1 5 s i

3. An Overview about Costs Databases

In the LCC, one of the initial steps is to know the quantities of services and resources consumed in the construction process, as well as their externalities (e.g., losses, waste, emissions, nuisances). An important tool to support this process is the so-called construction cost database. Construction cost database brings together the sectoral data on the demand for resources, services, and workers for constructive activities, also considering productivity (workers and resources). Such cost databases also standardize this data, supporting the quantification of services and budgeting of buildings. In general, cost databases are used to determine the price of services and the elaboration of construction budgets based on resource consumption rates (including losses) by activity and the quantitative list of activities from the project [22,24,39,40].

3.1. Applications of the Construction Cost Databases in Environmental Aspect Assessment

Table 2 presents a summary of the results of the literature review, by subject and environmental aspect, the environmental analysis method, cost databases, and their applications in the select study.
According to Table 2, the cost bases are present in studies of diverse environmental themes, such as waste generation, evaluation of construction materials, energy use, emission of pollution, water demand, occupational hazards and comparison among of constructive practices aiming at less impact. Figure 2 shows a cut-out of the analysis applied to the selected references. The cost databases have different applications and interact with environmental studies through different themes, materials, and methods.
These costs databases served as a source for the acquisition of quantitative data from constructive services or for description and qualitative analysis of the stages during the construction process. In the first case, the quantitative data obtained include the average consumption of resources (materials and services) and the estimation of losses and generation of construction and demolition waste (CDW) [7,41,42,52]. This estimate uses as an initial reference the provided budget and the description of its bills of quantities (BOQ) and applies over these the rates of the cost bases for consumption of resources and generation of waste per unit of service. In the second case, environmental studies use the structure of the unit compositions to identify the activities involved and to analyze the process flow (e.g., inputs/outputs, mass/energy). Among the themes in this group, the evaluation of the sustainability of the materials used [44,45], the comparison of construction systems and the proposition of more sustainable practices [49,50] as well as pollution emission and energy efficiency [11,15,51] can be considered.
The scope of the analysis depends on the steps addressed and the degree of detail in the description of the activities involved. Thus, the study can range from a specific stage to the entire life cycle of the built environment (construction, operation, maintenance, and deconstruction). In the case of carbon emissions, for example, some references address the stage of use of the building [6], while others refer to the construction process (from the preparation of the site to transportation and disposal of waste) [51].
The studies involving databases in Table 2 have applied different environmental assessments methods, some recurring in sustainability analysis such as life-cycle analysis, material flow analysis, and mass and energy balance. To a lesser extent, the use of more recent methodologies such as the Methodology for the Relative Sustainability Assessment of Residential Buildings—MARS-H [50,53] or Calificación Energética para Vivienda y Pequeños Edificios Terciarios (CALENER VYP) [51].
The structure and data extracted from the compositions of the cost databases support the description of activities and the quantification of their inputs and outputs in the studies with Material Flow Analysis (MFA) [54] and Material Input per unit of Service (MIPS) [36].
In addition to the cited scientific articles, sustainability guides and certification system also adopt cost databases to estimate losses and generation of construction waste. For example, material loss and productivity data from TCPO are present in the Casa Selo Azul certification of Caixa Econômica Federal [55] and waste generation data from GP CYPE are cited in the Best Environmental Management practice for the building and construction sector by Institute Prospective Technological Studies of the European Union [2].
Management tools often associated with the cost databases use are also shown in Table 2, such as Bills of Quantities [43], Gantt Chart and ABC Curve [46], and Material Flow Analysis [44].
Among the tools and cost databases are international databases, national and regional bases from different countries. While databases such as CYPE and RM Means have applications in several countries, others have national applications as a database of the Institute of Technology of Catalonia (BEDEC ITeC) [56], Base of Costs of the Construction of Andalusia (BCCA) [23] and Base of Prices of the Construction of the Community of Madrid—BCC [57] in Spain and the Fichas de rendimento by National Laboratory for Civil Engineering of Portugal (LNEC) [58].
In the Brazilian construction market, national and regional cost databases were cited [7,44,45,46,47], the Price Composition Table (TCPO) [24] and the National System of Cost and Construction Indexes Survey (SINAPI) [39], as well as a regional base, the Construction Budget System Sergipe (ORSE) [59], which has also been applied in other regions in studies and comparative studies [60].
Cross-analysis between the environmental concepts and tools versus traditional tools in construction management practices highlights the importance of bringing practice and environmental theory closer to construction activities, thereby increasing the reliability of results and identifying ways to reduce impacts of the construction process.

3.2. Use of Cost Bases into the Engineering Course Curriculums in Brazil

The documentary analysis identified only three construction cost databases in the 27 engineering courses analyzed, as described in Appendix B (Table A2). According to the findings, the Table of Compositions of Prices for Budgets (TCPO) is present in 21 of the 27 courses analyzed (78%), significantly higher than those for the National System of Costs Survey and Indexes of Civil Construction (SINAPI) cited by only 4 courses (11%) and the System of Referential Costs of Works (SICRO), 3 courses (7%).
In the course programs, such cost databases are associated with different themes and concepts (Table 3). Those subjects directly related to building budgets are among the most cited, such as the concepts of cost composition with 85%, and the direct and indirect costs (acronym BDI in Portuguese) with 67%. Nevertheless, the Basic Unit Cost (acronym CUB in Portuguese), an important sectoral indicator in Brazil, was found in only two courses, at the Federal University of Piaui (UFPI) and at the Federal University of Pampa (UNIPAMPA).
More broadly, cost databases are also used as a source of support for traditional construction planning and management tools. Among these techniques and tools, the most cited were the physical-financial schedule (85%), the analysis of interdependencies by PERT/CPM networks (67%), the use of resources by the ABC Curve (41%), the aggregation of costs over time by the S curve (33%), the analysis of the leveling of activities through the line-of-balance technique (33%), and the Gantt chart (26%) (Table 3).
Contrary to findings have observed in the literature review, in the programs and courses analyzed, few associations were found between environmental themes and cost databases, restricted to waste management in the course of the Federal Institute of Pernambuco (IFPE) and the evaluation of life-cycle costs in in the course of the Federal Institute of Paraiba (IFPB) (Table 3).
The survey identified many disciplines in which their course program contains the construction cost bases. Table 4 presents these disciplines grouped into three main areas: (a) management and planning; (b) project; (c) budget; and; (d) construction technologies.
To a lesser degree, some programs of transport courses also cite cost concepts and cost databases. the discipline Roads, these databases are often related to the stages and materials that comprise the execution of the construction services, as in the programs of the engineering course of the University of Brasília (UNB), Federal University of Amazonas (UFAM), Federal Institute of Rondonia), Federal University of Espirito Santo (UFES) and Federal University of Pampa (UNIPAMPA) in Rio Grande do Sul. In other cases, the contents were limited to the geometric design of the tracks, such as the Federal University of Goias (UFG), Federal University of Tocantins (UFT), Federal University of Santana Catarina (UFSC), Federal University of Piaui Federal University of Pernambuco (IFPE).
The analysis of the course programs (Table 4) also verified that they have a set of bibliographical references in common on subjects such as budget, management, and technology of the construction. Table 5 shows the top ten books, all related to the construction costs theme; these books have a strong influence on the education of Brazilian engineers and their practices.

3.3. Selection of Cost Databases Considering the State of Art and the State of Technic

According to the criteria established in the analysis of the research (Figure 1) (i.e., cross-analysis between the cost data bases most cited in the bibliographic review and the documental analysis of the course projects), six cost databases were selected for analysis (three international and three national). Figure 3 shows the flow adopted for the selection of databases and their main characteristics.
The first group brought together three Brazilian databases: Table of Price Compositions and Budgets (TCPO); National System of Research of Costs and Indices of the Civil Construction (SINAPI), and the System of Budget of Works of Sergipe (ORSE). The second group brought together three international bases: Generator of Price by CYPE; Base of Costs of the Construction of Andalusia(BCCA) [23]; e Base of Prices of the Construction of the Community of Madrid [57].
(a) Selected Brazilian cost databases - SINAPI, TCPO and ORSE—SINAPI, TCPO e ORSE
TCPO and SINAPI are considered the main bases of national coverage [44,45,71] while the ORSE is a base that has recently expanded its area of operation [7,60].
TCPO commercial database was launched by the PNI publisher in 1955, inspired by Master Format classification which is adopted in the United States and Canada [24] and currently presents a structure in five levels: division, subdivision, nature of the item, type and finally the item itself. The subdivision code describes the construction system, while the nature code describes whether the item is related to labor, material, equipment, financial costs or services [24]. TCPO brings together two databases (Buildings and Infrastructure) with more than 8500 unitary service compositions.
SINAPI is a public system of costs and indices of the construction industry. It was created in 1969 and has been maintained by Caixa Econômica Federal (CEF) and updated with prices collected by the Brazilian Institute of Geography and Statistics (IBGE) in the 27 federation units [39,60]. The SINAPI prices are a mandatory reference for budgeting and contracting of public works with resources of the Union in Brazil [72], including offering reference budgets for recurrent typologies in the construction sector.
The ORSE was developed by the State Housing and Public Works Company of Sergipe (CEHOP) and by the Sergipe Sanitation Company (DESO) [7,60,73]. According to its website, currently, the system has 9626 inputs and 9445 compositions registered for service prices [74].
(b) Selected international cost systems—CYPE, BCCA and BDCCM.
The Price Generator (GP CYPE) is a commercial cost database maintained by Cype Ingenieros [22] with versions adapted for 27 countries. The database assembles information on inputs and activities regarding pricing, construction techniques, waste generated, CO2 emissions, maintenance and operational risks [22]. The study chose the Brazilian version which presents data for three types of works: New Constructions, Reforms, and Infrastructure.
The Base of Costs of the Construction of Andalusia (BCCA) is maintained by Consejería de Obras Públicas y Vivienda (COPV) and Consejo Andaluz de Colegios de Aparejadores y Arquitectos Técnicos [43]. The BCCA, created in 2004, is a result of the systematization and classification of construction works in the region of Andalusia, action begun in 1884 by Fundación Codificación y Banco de Precios de la Construcción (FCBP) through the first Classification System [75]. The BCCA basic price classification comprises families and subfamilies.
The Base of Prices of the Construction of the Community of Madrid (BDCCM) was launched in 1991 and is periodically reassessed [57]. Its latest version was released in 2007 by Dirección General de Arquitectura y Vivienda de la Consejería de Medio Ambiente y Ordenación.

4. Results and Discussion about Costs Databases Assessment

4.1. The System of Classification and Quantification of Cost Bases

In general, the analyzed databases presented structures at hierarchical levels and descriptors to facilitate the consultation and editing, where their compositions can be accessed in block or individually. Such compositions are organized in steps (e.g., worksite preparation, foundations, structure, fence, installations and finish) which bring together similar building systems. In this sense, the BDCCM has a structure in four levels: area, chapter, subchapter, and group [57]. In turn, TCPO is structured in five levels: division, subdivision, nature of the item, type, and item [24]. Each TCPO composition has an individual coding, where the initial sequence represents the phase and the constructive system, and the next sequence indicates the labor, material, equipment, financial costs or activities. Among the building information classification systems adopted can be cited the Andalusia Construction Costs Database by the BCCA [76], the Normas Tecnológicas de la Edificación (NTE) by BDCCM [57] and the MasterFormat that served as the basis for TCPO [24].
The internal hierarchy of these systems of classification of works and services are directly related to the work breakdown structure (WBS). Thus, as observed in the review, the analytical budget generated according to these cost databases can also be used as a source to identify the constructive phases and the flow of materials and services (inputs and outputs) [7,44,45,77].
The productive resources can be inputs, machines, services, and labor. The indicators are used to qualify and quantify inputs and labor (description, unit of measure and cost), compositions (description, application, unit of measure and coefficients of consumption and labor) and expenses (direct or indirect). However, the wide variety of inputs and services regarding the nature and method of quantification makes aggregation and comparison difficult in environmental studies, for example, the quantification of inputs and outputs for mass and energy balance. This difficulty is partially circumvented through the adoption of equalization techniques when possible as can be observed in some of the cited articles of the review [41,42,43].

4.2. Findings from the Evaluation of Cost Bases

Table 6 presents the results of the environmental communication assessment matrix of the cost databases by themes and aspects (Table 1), Equations (1) and (2).
Figure 4 shows the standard results from the environmental communication performance evaluation model over the cost databases, as described in Table 6. To facilitate comparisons, radar diagrams for global values have been developed for each of the themes covered.

4.3. Interface (Information and Customization)

The six databases are similar in the records classification model and access through electronic sites. However, these same databases present significant differences in some features (e.g., database size, user interface, and communication of the results).
The analysis of the way in which the platform (interface) of the databases can help in the information management and environmental communication used adapted parameters of the PDCA cycle, it traditional in the evaluation of construction projects [78]. Thus, it was evaluated how the computerized systems and their data and information could contribute to the planning, application, control, and performance in the construction process. Some databases have an integrated computerized system for accessing their records and customizing information entries and exit. In these cases, the manipulation is through of a proprietary software (TCPO and ORSE) or directly in its electronic site (BDCCM). In other databases, the data is summarized in analytical compositions available only in a text file (BCCA) or worksheet (SINAPI) compatible with commercial electronic spreadsheets (e.g., Microsoft Excel).
Moreover, some electronic sites provide auxiliary documents which describe the methodology and classification system. For example, TCPO, ORSE and GP CYPE provide guidance on regulatory references, control procedures and measurement criteria. These regulations and control criteria are limited to issues of quality and safety and occupational health, these ignoring environmental impacts and annoyances generated. Those with computerized systems allow for some level of customization of their database (e.g., features of the enterprise, add new materials, change and create compositions). In the GP CYPE, the user can adjust the characteristics of the construction through the information such as built area, area and number of floors, accessibility and topography conditions, project type (e.g., single family, multifamily), distance to the licensed area for waste disposal, in addition to choosing between 20 types of plant geometry and land occupation.
Some of the systems (TCPO, ORSE and GP CYPE) present a set of construction management tools to support the planning and monitoring of services, tools such as the ABC curve, Gantt chart, and financial physical schedule. SINAPI and BBCA, in turn, do not allow the manipulation of data, only the consultation via an electronic website of the documents describing the service compositions, the methodology (memory), the systematic classification and the price updates collected.

4.4. Resources and Waste

In the selected cost databases, the productive resources comprise items such as materials, construction personnel, and equipment. In the service unit compositions, the concept of consumption adopted is the sum of the theoretical quantity needed for each resource plus the losses along the construction process (acquisition, stock, application) [24,60] related to local productivity. This quantity (theoretical and losses) defines the coefficient of consumption per service unit.
The BCCA adopts coefficients of consumption and productivity rates. The other bases (TCPO, ORSE, GP CYPE and BDCCM) allow the choice of consumption and productivity scales. This choice is in agreement with the concept of variable productivity [24,66,79], but limited to the economic dimension. Such an approach could be extended to the concept of environmental performance, which also influenced by productive factors (available technologies, staff qualification, and control systems). In the current model, the productivity range concept allows for estimating economic indicators (costs and time); however, it still does not allow to identify this variation about environmental aspects.
In the database structure, the traditional construction systems and materials, many of them with low environmental performance, are still prevalent, it is addressing the environmental and low impact materials only in isolated cases. In TCPO, for example, materials associated with occupational hazards such as asbestos cement tiles and pipes are listed. Only one chapter among the 17 BCCA addresses environmental services. Even this chapter (Waste Management) does not address the reduction or control of generation, limiting itself to an end-of-pipe control of waste removal: (a) metals, (b) asphalts and tarpaulins, (c) concrete, ceramics, and plaster. In the other bases (TCPO, SINAPI, ORSE, and BDCCM), no chapter was identified to gather such environmental services, those activities such as the removal of waste generated during land clearing or demolition are included in the Preliminary Services stage.
Only CYPE incorporates some system to classify the waste, using a national legal landmarks, Resolution 307 of 2002 by Brazilian National Council of Environment (CONAMA) [80] and Instruction n°13 by Brazilian Institute of Environment and Renewable Natural Resources (IBAMA) [81] besides estimating the mass and volume generated.
Even in those few cases where they address the materials and services which can support more sustainable practices, the communication of databases is still driven by the economic dimension. For example, incandescent lamps and LEDs (Light Emitting Diode) are differentiated by cost, while they could also be differentiated by energy efficiency criteria (e.g., energy consumption, lux, durability). In the reuse of materials, as in the case of concrete forms, the information contained in the databases refers more to the cost variation of the activity as a function of material consumption (wood or metal) than to the lower environmental impact.
Some progress can be seen in the adoption of those most popular building systems such as solar capture for thermal and photovoltaic applications. The CYPE GP and BDCCM provide chapters which bring together complete solar systems (capture, storage, and distribution) while on the ORSE only a few isolated activities. At the SINAPI base, in turn, no solar pickup services were identified, despite being an energy source that has been encouraged through financing from the Caixa Econômica Federal itself, the SINAPI maintainer.
It is observed that the few environmental actions identified in the databases have any associated economic advantage that is easily perceived by the builders or future users. This is the case in the cited examples of the use of more efficient light bulbs and the adoption of solar heating for showers (reduction of the energy bill), reuse of the forms of wood for concrete (reduction of the cost of acquiring wood).

4.5. Public Services (Urban Infrastructure)

The resources and services provided by the urban infrastructure (facilities) participate in the cost bases in a different way from those productive resources acquired in the construction suppliers (inputs and services). Inputs of origin in the construction market generally have their costs identified and quantified in each of the unitary compositions of which they are part. On the other hand, items such as water and energy are neglected despite these being present in most constructive activities and with significant environmental impacts [21].
In most of the bases, the consumption of water and energy are not quantified per service and are often considered as simple expenses linked to administrative activities. The lack of quantification of water and energy consumption makes it difficult not only to estimate the demand for these resources, but also makes it unfeasible to use control tools such as the ABC curve to analyze the total consumption [82,83], or the S curve to study their consumption over time [84].
An analysis of the compositions of the cited databases found that many of their processes demand water for various uses: as input to be added (e.g., production of concrete and mortar, dilution and paints); as facilitator (e.g., sprinklers control the humidity of aggregates and reduce dust emissions); and potable water for worker.
The results were classified and grouped by use and activities. The first group brought together the water use in traditional construction activities (e.g., foundation, structure, fences, and finishes), where it is usually incorporated into the constructive piece. The second group brought together those activities of higher water demand, such as earth moving, deep foundations and surface cleaning. The third group was the use of water by the construction site (e.g., to maintain its facilities and reducing dust) and drinking water consumption by workers.
In the first group (traditional constructive activities), only GP CYPE and BDCCM consider water consumption as a variable cost, which would allow analyzing both water demand per service and comparing it between different services. In the other bases analyzed (TCPO, SINAPI, and ORSE) water consumption is considered only as a fixed expense.
In the second group (services with high water demand), only the BCCA shows water as a variable cost in the unitary composition of the activities. However, the BCCA addresses the use of potable water even for earthmoving services, when it could encourage the use of reuse water, for example. A search on the BCCA identified 67 citations related to the potable water as an input, most of them in ground compaction services (using a tanker truck), foundation piles (by drilling or drilling), surface cleaning by blasting, landscaping. In the BDCCM and GP CYPE, the cost of water was not directly identified, only in those services of movement and compaction it is indirectly predicted through the cost of the tanker truck. In TCPO and ORSE the consumption and cost of water are not evidenced in their compositions.
Among the three, the third group of water use (construction site) was the one that showed less control over the water consumption, whereas the bases did not present indicators to monitor the water demand of the construction site activities.
The approach to energy consumption was like that applied to water consumption. Despite the use of energy is associated with those electrical machines and equipment (e.g., compressors, elevators, chainsaws) contained in the cost compositions, the analyzed bases considered the consumption of electric energy as an expense instead of a variable cost of the activity.
In the review of the environmental literature, some strategies seek to fill this lack of quantitative data to estimate water and energy consumption. Gangolells et al. [21] combined statistical data about water and energy consumption by area constructed with the quantities of construction services. Souza [46] estimated the water demand from standard quantities, services specifications, technical recommendations, and the worker numbers.

4.6. Machinery, Transport Services and Pollution

TCPO adopted the term “machines” for heavy equipment (e.g., excavators, cargo lifts, cranes, pile drivers) and the term “tool” for small equipment owned by the operator.
It was observed that in heavy-duty activities it is common for the composition to carry the name of the main machine. While, in those activities which involve vehicles to support their execution, the composition is named according to the function performed by these vehicles (transportation, loading, and unloading). In the databases, in general, the larger machines and vehicles and their compositions are grouped into specific chapters, such as the chapter “Machines, Vehicles and Equipment” in TCPO, “Infrastructure” in the ORSE, in the class “Cost machinery and equipment” at SINAPI, and “Machinery” at BCCA and BDCCM.
The circulation of machines and equipment contributes for generating several impacts and nuisances in the direct environment (neighborhood) and in the urban space. Among these externalities, it is the emission of smoke, noise, and vibration. However, the databases analyzed do not show environmental indicators that could be used to control these impacts.
Diesel oil consumption data by activity were identified in 129 TCPO compositions, wherein they consider the productive time of the machines and equipment. However, in these compositions, no references to associated terms such as “smoke” or “pollution” have been identified in their enforcement procedures. In the other bases (SINAPI, ORSE, CYPE, BCCA, and BDCCM), no fuel consumption data were found.
In the search, the term vibration was ordinarily associated with the description of those machines involved (e.g., self-propelled roller, vibratory plate compactor, immersion vibrator) or for achieving some requirements in the concrete pieces (e.g., density, consistency). In the databases, no vibration control procedures were identified, even for those pile driving and demolition activities. Exceptions were the activities involving the use of explosives and risks to the site and surrounding areas, which require planning the sequence of the service to reduce risks [24].
An alternative to estimating these aspects would be to use a combination of intensity and time factors. For example, fuel consumption would serve as a basis for estimating air pollution (burning of gases and smoke), noise generation rate to estimate noise pollution and the operating time of some machines to estimate nuisance from vibration.

4.7. Safety and Health (Occupational)

The analyzed cost databases present the same standard for labor classification and quantification. Demand for labor is classified according to the professional activity (e.g., masons, carpenters, electricians) which is assigned a unit cost per hour (man-hour).
The direct cost of labor is the sum of each professional’s time multiplied by their estimated time for that activity, also considering the productivity patterns inherent to the activity and the team and technologies involved [24]. Thus, knowing the amount of each activity may be extracted the workers’ times in a global way or by professional activity allowing to estimate the labor costs and to estimate the teams. In general, work safety programs use the size of these staffs and the risks normally associated with these professional activities to plan the demand for protective equipment (individual and collective), as well as for planning the training, supervision and control actions.
Considering that they adopt the professional profile as a key criterion for classifying the labor demand, the structure of these databases may lead users to ignore important factors such as working conditions and risk exposure. In their descriptions, the TCPO, ORSE and GP CYPE databases address the executive regulations and procedure of each activity applicable to environmental health and safety issues In the bases analyzed, the main safety standard is the NR-18 Working Conditions and Environment in the Construction Industry [85]. The description of the activities mentions several of the physical, chemical and biological hazards associated with the construction that are listed by NR-18 (e.g., electric shock, collapse, particle projection, explosion, falling objects, falling height).
However, quantitative data that would allow measuring these risks were not found, therefore, restricting the choice of safety measures according to subjective criteria. This approach does not distinguish those cases where the same activity performed under different conditions may present different risks. For example, the same exterior facade coating activity has different risks when performed on the ground floor compared to that performed on higher floors. In this sense, cost bases could, in addition to informing the risk according to the activity worker profile, also inform the risks according to the working conditions and exposure to the risk (e.g., fall in height, fall of objects).

4.8. Overall Results

Table 7 presents the normalized performance values by theme according to Equation (2) and the global values for each analyzed cost base obtained with Equation (3).
In general, cost databases were low performing in most aspects of environmental communication, especially data on water and energy consumption, use of machines and emission of pollution emission, and information related to occupational health and safety. The group consumption of water and energy was the one that presented the worst result according to the averages of performance of the selected cost bases. In fact, except for BCCA, the other bases consider water and energy consumption as an expense without presenting a method to quantify it as a function of the volume of activities.
Figure 5 shows the performance of each cost basis for the global values according to the defined evaluation aspects.
Considering the six bases, the CYPE Price Generator (GP CYPE) was the one that presented a better score, registering 3.1 points, followed by the Table of Compositions of Prices for Budgets (TCPO) of the Editora Pini and the System of Budget of Works of Sergipe (ORSE), both with 2.3 points.
In the group with the intermediate results were the regional bases of Spain, the Base of Prices of the Construction of the Community of Madrid (BDCCM) with 1.8 points and the Base of Costs of the Construction of Andalusia (BCCA), with 1.5 points. The worst performance was the National System for Costing and Indices of Civil Construction (SINAPI), with an overall performance of only 1 point.

5. Conclusions

This article performed an analysis of a set of cost bases for identifying relationships between cost data and environmental information. Firstly, it carried out a systematic review of the international literature on cost bases in environmental studies, followed by documentary analysis of the programs of the engineering courses to survey the most cited cost bases. This first step characterized the state of the art and state of the technique for definition of the collection and data analysis model. Then, an environmental communication assessment matrix was applied to the selected cost databases. Finally, the performance results of each cost base were compared.
The use of cost bases in environmental studies has been increasing in recent decades. However, as observed in the literature review applied, it was verified that such bases are adopted as an auxiliary tool to fill the lack of quantitative data in some instruments of environmental assessment. Thus, from the structure and data of these cost databases are extracted information which combined with environmental analysis tools allow for obtaining environmental indicators such as consumption of resources (materials, water, and energy), generation of waste and pollution emission. This process could be better systematized if the cost bases incorporated direct environmental indicators instead of requiring correlations with other instruments. This action would also improve the dissemination of environmental information among its users.
A documentary analysis has identified that such cost databases are one relevant content in the education of Brazilian civil engineering according to the pedagogical projects of their courses. However, it was observed a concentration in few bases and a low integration with environmental themes. Although the analysis was applied to a wide range of courses (one for each of the 27 units of the Brazilian federation) to cover possible regional differences, the results show that the citations are restricted to only three bases, all of them of national scope: the Price Composition Table (TCPO), the National System of Costs Survey and Indices of Civil Construction (SINAPI), and the System of Reference Costs of Works (SICRO). Among the three bases cited by the 27 Brazilian courses selected, TCPO obtained the highest number of citations, with 21 occurrences (78%), well above SINAPI, with 4 cases, and SICRO, with only 3 cases.
In contrast, while in the analysis of the programs of the courses in Brazil the bases mentioned were national in scope, in the review of the literature, the regional bases in Spain prevailed, such as the Base of Costs of the Construction of Andalusia (BCCA) and the Base of Prices of the Construction of the Community of Madrid (BCCM).
Other findings come from the asymmetry of the correlation of databases with topics such as construction management and environmental management. The cost databases have a high affinity with themes such as physical-financial planning of the work, 85% of the cases. However, the same databases present an association of only 7% to environmental issues, such as waste management (1 case) and life-cycle assessment (1 case). These results point to the need to revise the course programs as a strategy to improve the insertion of the environmental dimension in the education of engineers and in their professional practice.
Finally, the application of the evaluation matrix of the environmental communication allowed mapping the performance of the cost bases according to the selected themes and the comparison among those. It was observed that, although the analyzed cost bases have similar structures for the classification of the records, they are very different as regards the quality of the environmental information according to the evaluation criteria applied by research.
The CYPE Price Generator, international coverage, presented the best results followed by TCPO, national coverage, both cost bases are maintained by private institutions. The ORSE registered the third best performance, which is maintained by the public sector and of regional coverage (State of Sergipe in Brazil). The second group had the worst performers. The regional bases of Spain, Base of Costs of the Construction of Andalusia (BCCA) and Base of Prices of the Construction of the Community of Madrid (BDCCM), had intermediate performance. The National System for Research in Costs and Indices of Civil Construction (SINAPI), maintained by public agent, registered the worst performance among the six cost bases analyzed.
It is important to note that the bases of the regions of Spain of Andalusia and Madrid are part of initiatives of local governments to promote the improvement of the performance of the regional construction sector. Such a strategy could be extended to improve tools in other local contexts. SINAPI in Brazil has a great potential for disseminating environmental information in the national construction sector as it is a mandatory reference in constructions financed with federal government resources and has a wide data collection structure, maintained by the Caixa Econômica Federal (CEF) and by the Brazilian Institute of Geography and Statistics (IBGE).
According to the results, the use of computerized systems can contribute to improved access to data, the search for indicators and the generation of more complete reports aimed at improving the quality of information and guiding building practices. In this sense also, the sector in Brazil needs a consolidated model for the classification of construction data in order to facilitate the collection and communication of data to users and other management systems. The agents involved in the development of these tools have an important role in this action, considering that these systems reach a large public of users of the construction sector, comprising students in training (graduates and technicians), budgeting, planning engineers and managers.
The results point to the confirmation of the initial hypothesis, in which traditional tools such as cost bases can contribute beyond the economic management of the construction process. These cost bases, incorporating new indicators, can help to plan and control local impacts and increase the environmental awareness of construction agents aiming at lower impact sites.

Author Contributions

L.C.A.B., S.F.C., and A.K. conceived the study and designed the conceptual research framework. L.C.A.B. performed the data collection and analysis. S.F.C., R.D.A.C., and A.K. reviewed the analysis. L.C.A.B. wrote the paper. S.F.C., R.D.A.C., and A.K. reviewed the final version of the manuscript.

Funding

This research received no external funding.

Acknowledgments

The authors acknowledgments the important collaboration of Clean Technology Network (TECLIM) of the Department of Environmental Engineering at Federal University of Bahia (UFBA), and the Federal Institute of Bahia (IFBA). The authors are also grateful for the contributions of Juan Pedro Moreno Delgado of the Federal University of Bahia and João Luiz Calmon Nogueira da Gama of the Federal University of Espirito Santo.

Conflicts of Interest

The authors declare no conflict of interest.

Abbreviations

BCCABase de Costes de la Construcción de Andalucía (in Spanish)
BDCCMBase de Datos de la Construcción de la Comunidad de Madrid (in Spanish)
GP CYPEGenerador de precios da Cype Ingenieros (in Spanish)
LNECLaboratório Nacional de Engenharia Civil (in Portuguese)
ORSESistema de Orçamento de Obras de Sergipe
SICROSistema de Custos Referenciais de Obras
SINAPISistema Nacional de Pesquisa de Custos e Índices da Construção Civil
TCPOTabela de Composições de Preços para Orçamentos

Appendix A

Table A1. Websites consulted to obtain Civil Engineering Course Projects and their programs by Brazilian regions, federation units and Education Institutions (Authors, 2018).
Table A1. Websites consulted to obtain Civil Engineering Course Projects and their programs by Brazilian regions, federation units and Education Institutions (Authors, 2018).
RegionUFInstitutionAcronymWebsite
NorthACFederal University of AcreUFAChttps://portal.ufac.br/ementario/curriculo.action?v=335
APFederal University of AmapaUNIFAPhttp://biblioteca.ufam.edu.br/attachments/article/259/Projeto%20Pedag%C3%B3gico%20curso%20Engenharia%20Civil.compressed.pdf
AMFederal University of AmazonasUFAMhttp://www2.unifap.br/engcivil/files/2014/01/PPC-Civil-Final-16_10_12.pdf
PAFederal University of Pará UFPAhttp://www.camtuc.ufpa.br/index.php/engenharia-civil
ROFederal Institute of Rondônia IFROhttp://portal.ifro.edu.br/calama/cursos/4719-engenharia-civil
RRFederal University of RoraimaUFRRhttp://ufrr.br/engcivil/index.php?option=com_phocadownload&view=category&id=11:disciplinas&Itemid=312
TOFederal University of TocantinsUFThttp://www.uft.edu.br/centroengenharias/ementas/
NortheastALFederal University of AlagoasUFALhttps://ufal.br/estudante/graduacao/projetos-pedagogicos/campus-maceio/ppc-eng-civil.pdf
BAFederal University of BahiaUFBAhttp://www2.eng.ufba.br/site/index.php/civil/ementas
CEFederal University of CearaUFChttp://www.deecc.ufc.br/Download/
MAFederal University of MaranhãoUFMAhttp://www.ccec.ufma.br/index.php/projeto-
PBFederal Institute of ParaíbaIFPBhttps://estudante.ifpb.edu.br/media/cursos/25/documentos/PPC_Engenharia_Civil-CZ.pdf
PEFederal Institute of PernambucoIFPEhttps://portal.ifpe.edu.br/campus/recife/cursos/superiores/bacharelados/engenharia-civil/projeto-pedagogico
PIFederal University of PiauíUFPIhttp://www.leg.ufpi.br/subsiteFiles/cc/arquivos/files/eng_civil_cmpp.pdf
RNFederal University of Rio Grande do NorteUFRNhttps://sigaa.ufrn.br/sigaa/public/curso/ppp.jsf?lc=pt_BR&id=2000025
SEFederal University of SergipeUFShttp://www.ifs.edu.br/cursos-superiores/259-cursos/superiores/4306-bacharelado-em-engenharia-civil#ppc
MidwestDFUniversity of BrasíliaUNBhttps://matriculaweb.unb.br/graduacao/oferta_dis.aspx?cod=162
GOFederal University of GoiásUFGhttp://www.eec.ufg.br/up/140/o/Eng_Civil_Anexo_II_Ementas_e_Bibliografica_Grade_2009-1.pdf
MTFederal University of Mato GrossoUFMThttps://www.ufmt.br/ufmt/site/ensino/consultaPlanoEnsino/Cuiaba
MSFederal University of Mato Grosso do SulUFMShttp://engenhariacivil.sites.ufms.br/curso-2/projeto-pedagogico/
SoutheastESFederal University of Espírito SantoUFEShttp://www.engenhariacivil.ufes.br/projeto-pedag%C3%B3gico-e-estrutura-curricular
MGFederal University of Minas GeraisUFMGhttps://www.eng.ufmg.br/portal/
RJFederal University of Rio de JaneiroUFRJhttps://www.siga.ufrj.br/sira/temas/zire/frameConsultas.jsp?mainPage=/repositorio-curriculo/F011BEAD-92A4-F79A-2A99-E698E5E08ACF.html
SPUniversity of São PauloUSPhttps://uspdigital.usp.br/jupiterweb/
SouthPRFederal University of Technology–Parana/BrazilUTFPRhttp://www.utfpr.edu.br/curitiba/cursos/bacharelados/Ofertados-neste-Campus/engenharia-de-producao-civil/planos-de-ensino
RSFederal University of PampaUNIPAMPAhttp://www.unipampa.edu.br/portal/documentos
SCFederal University of Santa CatarinaUFSChttp://ecv.paginas.ufsc.br/files/2014/06/Projeto_Pedagógico_2014.pdf

Appendix B

Table A2. Disciplines of selected civil engineering courses related to cost databases by Brazilian regions, states and Education Institutions (Authors, 2018).
Table A2. Disciplines of selected civil engineering courses related to cost databases by Brazilian regions, states and Education Institutions (Authors, 2018).
RegionUFInstitutionAcronymCurricular Components that Cite Cost DatabasesDatabase
NorthACFederal University of AcreUFACConstruction Management/Administration/Construction Budget/Construction Planning/Control
APFederal University of AmapaUNIFAPConstruction Budget/Construction Planning and Management/Construction Technology I and IITCPO
AMFederal University of AmazonasUFAMCivil Construction II/Road Construction and Land WorksTCPO, SICRO.
PAFederal University of Pará UFPAConstruction Budget/Construction Planning and Management II/Coatings TechnologyTCPO, SICRO, SINAPI
ROFederal Institute of Rondônia IFROConstruction BudgetTCPO
RRFederal University of RoraimaUFRRCivil Construction/Construction planning and controlTCPO
TOFederal University of TocantinsUFTBuilding Construction Technology II/Construction planning and control_
NortheastALFederal University of AlagoasUFALManagement of construction projects/Planning and management of production in construction/Construction Technology I and II _
BAFederal University of BahiaUFBACivil Construction I and II/Administration applied to Civil EngineeringTCPO
CEFederal University of CearaUFCBuilding Construction I/Cost Planning/Construction ManagementTCPO
MAFederal University of MaranhãoUFMABudget/Construction Planning and Control/Civil Construction I and IITCPO
PBFederal Institute of ParaíbaIFPBLife cycle costing/Construction planning and budgetingTCPO
PEFederal Institute of PernambucoIFPESpecifications and budget/Construction management/Production planning and controlTCPO
PIFederal University of PiauíUFPIAdministration applied to Engineering/Building Construction/Construction Planning and Control/Construction Equipment TCPO, SICRO
RNFederal University of Rio Grande do NorteUFRNCivil Construction 2/Construction ManagementTCPO
SEFederal University of SergipeUFSPlanning and Management in Production of Buildings/Construction BudgetTCPO
MidwestDFUniversity of BrasíliaUNBConstruction Technology I/Construction Planning and Control/Road DesignTCPO, SICRO
GOFederal University of GoiásUFGCivil Construction 1 and 2/Construction Planning and ControlTCPO
MTFederal University of Mato Grosso UFMTPlanning Techniques in Civil Construction_
MSFederal University of Mato Grosso do SulUFMSCivil Construction/Civil Construction Management/ Construction Planning/Quality in Civil ConstructionTCPO
SoutheastESFederal University of Espírito Santo UFESManagement of Civil Construction/Project Management,
MGFederal University of Minas GeraisUFMGCivil Construction Management/Construction Technology 1 and 2 TCPO
RJFederal University of Rio de JaneiroUFRJBuildings/Construction Management/Project Management/Construction Planning.TCPO
SPUniversity of São PauloUSPManagement of Construction Production/Planning and Construction Costs/Civil Construction I and II
SouthPRFederal University of Technology—ParanaUTFPRSpecifications and budgets/Project management. Construction management/Heavy construction work.TCPO. SINAPI
RSFederal University of PampaUNIPAMPABudget and construction scheduling/Construction Management/Design of road structures.TCPO
SCFederal University of Santa Catarina UFSCConstruction Management/Civil Construction Techniques IITCPO, SICRO

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Figure 1. Research workflow.
Figure 1. Research workflow.
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Figure 2. Network of correlations between Themes, Materials and Methods, Databases and their Applications by analyzed articles.
Figure 2. Network of correlations between Themes, Materials and Methods, Databases and their Applications by analyzed articles.
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Figure 3. Databases selected and their main characteristics (Authors, 2018).
Figure 3. Databases selected and their main characteristics (Authors, 2018).
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Figure 4. Performance of cost databases by the Environmental Communication Assessment Matrix. Description of radar diagrams by themes: (a) overall result about 5 themes; (b) information and communication; (c) resources consumption and waste generation; (d) water and energy consumption; (e) machinery and pollution; (f) health and safety.
Figure 4. Performance of cost databases by the Environmental Communication Assessment Matrix. Description of radar diagrams by themes: (a) overall result about 5 themes; (b) information and communication; (c) resources consumption and waste generation; (d) water and energy consumption; (e) machinery and pollution; (f) health and safety.
Sustainability 11 00187 g004aSustainability 11 00187 g004b
Figure 5. Radar diagrams for Environmental Communication Assessment. Notes: Information and Communication (I/C), Resources consumption and Waste generation (RC/WG), Water and Energy Consumption (WC/EC), Machinery Circulation and Pollution Emissions (MC/PE), Healthy and Safety Occupational (H/S).
Figure 5. Radar diagrams for Environmental Communication Assessment. Notes: Information and Communication (I/C), Resources consumption and Waste generation (RC/WG), Water and Energy Consumption (WC/EC), Machinery Circulation and Pollution Emissions (MC/PE), Healthy and Safety Occupational (H/S).
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Table 1. Environmental Communication Assessment Matrix (ECAM) to Costs Databases.
Table 1. Environmental Communication Assessment Matrix (ECAM) to Costs Databases.
Theme (a)/Indicator (b)w = 0 (c)w = 1w = 2
IC Information and Communication
IC1 user interfacepresswebweb and software
IC2 acquisitionannual licenselicense limited (free) or full (paid)free no restrictions
IC3 reported featuresconsumption rate, unitary compositionsconsumption rate, unitary compositions, and proceduresconsumption rate, unitary compositions, procedures, and specifications
IC4 parameterized projectnot providedconstruction size or environmental conditionsconstruction size and environmental conditions
IC5 parametrized activitiesnot providedby materials or work conditionsby materials and work conditions
IC6 customization of databasenot providedlocal priceslocal prices, new materials, and new activities
IC7 reported resultsnot providedoverall quantitiesoverall quantities and reports (e.g., Gantt diagram, ABC curve)
RW Resources consumption, and waste generation
RW1 systems more sustainablenot providedsome caseschapter of systems more sustainable
RW2 certificated woodnot informedinformed in specificationprovide to selection
RW3 recycled materialsnot providedconcrete or aggregates concrete, aggregates and others
RW4 other materials more sustainablenot providedsome casesgroup of materials more sustainable
RW5 waste managementnot providedonly collection and removal of wastewaste management (control of generation, separation and collection)
RW6 waste generatednot providedestimate in percentageestimate by mass and volume
RW7 waste classificationnot providednot standardizednational standard
PS Public services
PS1 water consumption for productionnot providedestimated by traditional services except earthworkestimated by traditional services and earthwork
PS2 water consumption for workersnot providedestimated by traditional services or earthworkestimated by traditional services and earthwork
PS3 electric energy consumptionnot providedestimated by services except earthworkestimated by services and earthwork
MP Machinery, and pollution emissions
MP1 circulation of machinery and vehiclesnot providedaddressed in auxiliary activity (productivity by average distance)addressed in main activity (productivity by average distance)
MP2 fuel consumptionnot providedestimated by earthwork servicesestimated by earthwork and traditional services
MP3 noise/vibration emission equipmentnot providedinformed but not quantifiedinformed and quantified
MP4 noise level informationnot providedin the activity descriptionin the activity and the control actions
HS Health and safety
HS1 demands of workersnot informedby activityby activity and global
HS2 requirements for occupational risksnot informedregulatory requirementsregulatory requirements, and procedures
H3 classification of the occupational risksnot informedby type workersby workers type and exposed risk
(a) selected themes adapted from EMAS, Chen et al., (2000) Gangolells et al., (2009), and Mateus; Bragança (2011). (b) indicators during the construction phase. (c) Weight scale (w) adopted to characterize the quality of the environmental information of the data available on the cost databases, where w can be 0 (no information or low quality), 1 (partial information) and 2 (wide information).
Table 2. Applications of cost databases on environmental literature.
Table 2. Applications of cost databases on environmental literature.
ReferenceTheme (Aspect)MethodDatabaseApplication of the Cost Databases
[7]CDW (estimate in urban infrastructure projects)LCA. LCC. Design optimizationTCPO, ORSE, SINAPIIdentification of the construction systems and waste generated based on the budget.
[41]CDW (on-site generation indicators)Estimate for mass/area. Units EqualizationGP CYPEEstimate amount of CDW per built area.
[42]CDW (estimate on the design stage)LCA. Units Equalization.BCCAEstimate waste and loss during construction
[43]CDW (quantification and management)BOQ. Units Equalization.BCCAEstimate CDW per service unit.
[44]Environmental impacts of building materialsLCA. Case study.
Material and energy flow.
TCPO, SimaProIdentification of the inputs and outputs flow. Estimate materials consumption per service unit.
[45]Environmental impacts of building materialsLCA. Case Study.TCPO, SimaProEstimate materials consumption per service unit
[46]Water footprint (estimate on the construction)Curve ABC.
Gantt Chart.
TCPOEstimate the water consumption per service to determine the water footprint in construction processes
[47]Environmental impacts of construction systemsLCASINAPI, SimaPro, EcoinventIdentification of the inputs and outputs flow. Estimate materials consumption per service unit.
[48]On-Site Environmental Impacts and Health and Safety RiskISO 14001:2004
OHSAS 18001:2007
ITeCTo Identify the work sections in the construction of residential buildings
[49]More sustainable construction (comparison of costs)CESSUC. Case Study.InterPro 2010Estimate and comparing the referential construction costs about more sustainable constructions.
[50]More sustainable construction (sustainable practices)LCA. MARS-HFichas by LNEC Quantification for comparison between traditional and more sustainable construction
[11]Energy retrofit of historic buildingsCost optimally, LCA and LCCGP CYPEGetting of costs (materials, systems, operation, and maintenance) to analyses the cost optimality.
[51]Energy and Emissions Impact (Housing)LCA. Emissions balance.GP CYPE, LIDER + CALENER.Estimate urbanization and maintenance costs generated from the housing projects
[6]Energy Efficiency and Carbon emissions (news buildings)LCA. LCC. Integrated designRS MeansEstimate the cost implications of energy-based carbon emissions
[15]Energy Efficiency and Carbon emissions (building renovation)LCC. Annex 56 by IEA EBC.GP CYPEEstimate of the investment, maintenance, and replacement costs in building renovation
Notes: (a) Themes: Construction and Demolition Waste (CDW). (b) Methods: Life Cycle Assessment (LCA), Life Cycle Cost (LCC), Bill of Quantities (BOQ), Método de Evaluación de la Vivienda Sustentable (CESSUC); Metodologia de Avaliação Relativa da Sustentabilidade de Edifícios de Habitação (MARS-H); International Energy Agency Energy in Buildings and Communities (IEA EBC). (c) Databases: Tabela de Composições de Preço (TCPO); o Sistema Nacional de Pesquisa de Custos e Índices da Construção Civil (SINAPI)—SINAPI e o Sistema de Orçamento de Obras de Sergipe (ORSE); Gerador de Preços CYPE (GP CYPE); Base de Costes de la Construcción de Andalucía (BCCA); Laboratório Nacional de Engenharia Civil (LNEC); Calificación Energética para Vivienda y Pequeños Edificios Terciarios (CALENER VYP); Limitación de Demanda Energética (LIDER).
Table 3. Themes and concepts associated with the use of cost databases in the selected courses.
Table 3. Themes and concepts associated with the use of cost databases in the selected courses.
Themes and ConceptsRecords%
(a) Budget-related concept and indexes
      Compositions of unit costs2489%
      Bonus and Indirect Costs (BDI acronym in Portuguese)1867%
      Basic Unit Cost (CUB acronym in Portuguese) (in UFPI, UFMT and UNIPAMPA)311%
(b) Management-related techniques and tools
      Physical-financial schedule2385%
      PERT/CPM1867%
      ABC-Curve1141%
      S-Curve933%
      Line of Balance (LOB)933%
      Gantt Chart726%
(c) Other themes
      Construction-site layout622%
      Lean construction (in UFAL, UFES and, UFMG)311%
      Waste management (in IFPE)14%
      Life-cycle cost assessment (in IFPB)14%
Notes: Federal University of Piaui (UFPI); Federal University of Mato Grosso (UFMT); Federal University of Pampa (UNIPAMPA); Federal University of Alagoas (UFAL); Federal University of Espirito Santo (UFES); Federal University of Minas Gerais; Federal Institute of Paraiba (IFPB). Source: Documentary analysis of Pedagogical Projects of Courses—PPC (Authors, 2018).
Table 4. Courses whose programs refer to the cost databases.
Table 4. Courses whose programs refer to the cost databases.
SubjectCoursesRecords%
Management and PlanningConstruction planning. Construction management. Planning and control of works. Planning and construction management.1874%
Production control. Control of the construction process830%
Quality of Construction (in UFMS and UFG)27%
Construction loss control (in UFPI)14%
DesignCivil Construction Project. Design of Buildings I. Project management (in UFC and UFRJ)27%
Budgeting and LCCBudget in construction. Costs management. Specifications and budgets.1348%
Construction TechnologyConstruction I and II. Construction of building I and II.1348%
Technology of construction I and II.726%
Notes: Federal University of Mato Grosso (UFMT); Federal University of Goias (UFG); Federal University of Piaui (UFPI); Federal University of Ceara (UFC); Federal University of Rio de Janeiro (UFRJ). Source: Documentary analysis of Pedagogical Projects of Courses—PPC (Authors, 2018).
Table 5. 10 Most cited books in the course program related to cost databases.
Table 5. 10 Most cited books in the course program related to cost databases.
Authors and Book (in Portuguese)Records%
LIMMER, C V. Planning, budgeting and control of projects and works [61].2281%
YAZIGI, Walid. The technique of building [62].1556%
TISAKA, M. Budget in construction: consulting, project and execution [63].1348%
BERNARDES, M. Production control planning for construction companies [64].1244%
GOLDMAN, Pedrinho. Introduction to planning and cost control in Brazilian civil construction [65].1037%
MATTOS, A. D. How to prepare construction budgets [66].1037%
MATTOS, A. D. Planning and control of construction [67].933%
GIAMUSSO, S. E. Budget and Costs in Construction [68].933%
DIAS, Paulo R. V. Cost engineering: a budgeting methodology for civil constructions [69].830%
GUEDES, Milber F. Caderno de encargos (title in Portuguese) [70].726%
Source: Documentary analysis of Pedagogical Projects of Courses—PPC (Authors, 2018).
Table 6. Results of the environmental communication assessment matrix (Authors, 2018).
Table 6. Results of the environmental communication assessment matrix (Authors, 2018).
Information and CommunicationTCPOSINAPIORSECYPEBCCABDCCM
user interface211201
acquisition022222
reported features202211
parameterized project000202
parametrized activities202200
customization of database202201
reported results202200
Score (S1)103111437
Maximum score possible141414141414
Standard score (s1)0.70.20.81.00.20.5
Resources Consumption and Waste GenerationTCPOSINAPIORSECYPEBCCABDCCM
systems more sustainable101212
certificated wood 000000
recycled materials101111
other materials more sustainable101212
CDW management (services)111221
CDW generated101211
CDW classification000200
Score (S2)5151167
Maximum score possible141414141414
Standard score (s2)0.40.10.40.80.40.5
Water and Energy ConsumptionTCPOSINAPIORSECYPEBCCABDCCM
water consumption for production000121
water consumption for workers000000
electric energy consumption000000
Score (S3)000121
Maximum score possible666666
Standard score (s3)0.00.00.00.20.30.2
Machinery Circulation and Pollution EmissionsTCPOSINAPIORSECYPEBCCABDCCM
circulation of machinery and vehicles111111
fuel consumption110000
noise/vibration emission equipment222222
noise level information000000
Score (S4)443333
Maximum score possible888888
Standard score (s4)0.50.50.40.40.40.4
Health and SafetyTCPOSINAPIORSECYPEBCCABDCCM
Demand of workers212211
requirements for occupational risks202200
classification of the occupational risks000000
Score (S5)414411
Maximum score possible666666
Standard score (s5)0.70.20.70.70.20.2
Table 7. Overall value (G) of the performance of the cost databases.
Table 7. Overall value (G) of the performance of the cost databases.
ThemeTCPOSINAPIORSECYPEBCCABDCCMAverage
IC0.70.20.81.00.20.50.6
RC/WG0.40.10.40.80.40.50.4
WC/EC0.00.00.00.20.30.20.1
MC/PE0.50.50.40.40.40.40.4
H/S0.70.20.70.70.20.20.5
Sum (G)2.31.02.33.11.51.8
Notes: Information and Communication (I/C), Resources consumption and Waste generation (RC/WG), Water and Energy Consumption (WC/EC), Machinery Circulation and Pollution Emissions (MC/PE), Healthy and Safety Occupational (H/S).

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Borja, L.C.A.; César, S.F.; Cunha, R.D.A.; Kiperstok, A. Getting Environmental Information from Construction Cost Databases: Applications in Brazilian Courses and Environmental Assessment. Sustainability 2019, 11, 187. https://doi.org/10.3390/su11010187

AMA Style

Borja LCA, César SF, Cunha RDA, Kiperstok A. Getting Environmental Information from Construction Cost Databases: Applications in Brazilian Courses and Environmental Assessment. Sustainability. 2019; 11(1):187. https://doi.org/10.3390/su11010187

Chicago/Turabian Style

Borja, Luis Claudio A., Sandro Fábio César, Rita Dione A. Cunha, and Asher Kiperstok. 2019. "Getting Environmental Information from Construction Cost Databases: Applications in Brazilian Courses and Environmental Assessment" Sustainability 11, no. 1: 187. https://doi.org/10.3390/su11010187

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