roles of social impact assessment practitioners

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Roles of social impact assessment practitioners Cecilia H.M. Wong , Wing-chung Ho 1 Department of Applied Social Sciences, City University of Hong Kong, Hong Kong Special Administrative Region abstract article info Article history: Received 2 August 2013 Received in revised form 9 September 2014 Accepted 12 September 2014 Available online xxxx Keywords: Social impact assessment practitioner Professional role Project management Community development Public involvement Systematic review The effectiveness of social impact assessment (SIA) hinges largely on the capabilities and ethics of the practi- tioners, yet few studies have dedicated to discuss the expectations for these professionals. Recognising this knowledge gap, we employed the systemic review approach to construct a framework of roles of SIA practi- tioners from literature. Our conceptual framework encompasses eleven roles, namely project manager of SIA, practitioner of SIA methodologies, social researcher, social strategy developer, social impact management consul- tant, community developer, visionary, public involvement specialist, coordinator, SIA researcher, and educator. Although these roles have been stratied into three overarching categories, the project, community and SIA development, they are indeed interrelated and should be examined together. The signicance of this study is threefold. First, it pioneers the study of the roles of SIA practitioners in a focused and systematic manner. Second, it informs practitioners of the expectations of them thereby fostering professionalism. Third, it prepares the public for SIAs by elucidating the functions and values of the assessment. © 2014 Elsevier Inc. All rights reserved. Introduction Social impact assessment (SIA) is a strategic tool for managing the social consequences of development. Through analysing and monitor- ing the social change processes and social impacts of planned interven- tions, it fosters the sustainability and equitability of the biophysical and human environment (Vanclay, 2003). For its value in promoting cost- effectiveness in the long run, SIA has been applied to an array of arenas such as dam construction (e.g. Wang et al., 2013), mining (e.g. Lockie, 2009), land use management (e.g. Tilt et al., 2009), food control (e.g. Dreyer et al., 2010), agriculture (e.g. Bournaris and Manos, 2012), shery (e.g. Pollnac et al., 2006), sports (e.g. Burnett, 2001), transportation and procurement (e.g. Esteves and Barclay, 2011), public management (Antonie, 2012), supply chain management (Esteves et al, 2012) and disaster management (e.g. Kumagai et al., 2006). Given this wide application, the practitioners of SIA also come from a wide spectrum of disciplines (Baines et al., 2013; Morgan et al., 2012). Practitioners, in this context, refer to the people who practice the methodology of SIA and undertake associated social and environmental research to inform the practice of SIA(Vanclay, 2003; p. 2). They usually rst have training in other professions, then learn and practice SIA methodologies. Corresponding to the purposes and context of SIAs, the types of prac- titioners vary. For example, in the SIAs conducted by corporations to seek social license for their development projects, the practitioners can be the internal staff or external private consultants. In the commu- nity initiated SIAs, the practitioners can be the community members or consultants hired from universities (Vanclay, 2003). As SIA is a trans-disciplinary social science which requires knowl- edge ranging from sociology, anthropology, demography to environ- mental law (Esteves et al., 2012); the exercises usually employ a team approach so that each professional can contribute their expertise and make the best use of inter-professionalism (Morgan et al., 2012; Vanclay, 2003). While all SIAs are generally guided by the International Principles for Social Impact Assessment (the Principles), each practice is case-specic (Vanclay, 2003). The selection of study scope and targets, the adaptions of methods, and the formulation of plans all demand a sensitive and exible use of SIA theories and methods. Hence, the quality of SIAs is largely, though not solely, determined by the ethics and capabilities of the practitioners. Literature shows how the inadequacies and malpractices of practi- tioners hamper the effectiveness of SIAs. For example, Suopajärvi (2013) reported that by failing to perform a thorough scoping, the prac- titioners resulted in leaving some vulnerable groups in the impact areas unassessed. Burdge and Johnson (1994) revealed that some practi- tioners refused to conduct primary research for saving cost and time; hence their research lacked empirical evidence. Harvey et al. (2011) also called for attention to the misconduct of deliberately shaping a favourable public opinion by controlling the content, structure and organisation of public engagement. Goldenberg and Frideres (1986) Environmental Impact Assessment Review 50 (2015) 124133 Corresponding author at: Unit 210, 1 Queens Avenue, Hawthorn, Victoria 3122, Australia. Tel.: +61 490244587. E-mail addresses: [email protected] (C.H.M. Wong), [email protected] (W. Ho). 1 City University of Hong Kong, Tat Chee Avenue, Kowloon, Hong Kong Special Administrative Region. Tel.: +852 34428134. http://dx.doi.org/10.1016/j.eiar.2014.09.008 0195-9255/© 2014 Elsevier Inc. All rights reserved. Contents lists available at ScienceDirect Environmental Impact Assessment Review journal homepage: www.elsevier.com/locate/eiar

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Environmental Impact Assessment Review 50 (2015) 124–133

Contents lists available at ScienceDirect

Environmental Impact Assessment Review

j ourna l homepage: www.e lsev ie r .com/ locate /e ia r

Roles of social impact assessment practitioners

Cecilia H.M. Wong ⁎, Wing-chung Ho 1

Department of Applied Social Sciences, City University of Hong Kong, Hong Kong Special Administrative Region

⁎ Corresponding author at: Unit 210, 1 Queens AvenAustralia. Tel.: +61 490244587.

E-mail addresses: [email protected] (C.H.M.(W. Ho).

1 City University of Hong Kong, Tat Chee Avenue,Administrative Region. Tel.: +852 34428134.

http://dx.doi.org/10.1016/j.eiar.2014.09.0080195-9255/© 2014 Elsevier Inc. All rights reserved.

a b s t r a c t

a r t i c l e i n f o

Article history:Received 2 August 2013Received in revised form 9 September 2014Accepted 12 September 2014Available online xxxx

Keywords:Social impact assessment practitionerProfessional roleProject managementCommunity developmentPublic involvementSystematic review

The effectiveness of social impact assessment (SIA) hinges largely on the capabilities and ethics of the practi-tioners, yet few studies have dedicated to discuss the expectations for these professionals. Recognising thisknowledge gap, we employed the systemic review approach to construct a framework of roles of SIA practi-tioners from literature. Our conceptual framework encompasses eleven roles, namely project manager of SIA,practitioner of SIAmethodologies, social researcher, social strategy developer, social impactmanagement consul-tant, community developer, visionary, public involvement specialist, coordinator, SIA researcher, and educator.Although these roles have been stratified into three overarching categories, the project, community and SIAdevelopment, they are indeed interrelated and should be examined together. The significance of this study isthreefold. First, it pioneers the study of the roles of SIA practitioners in a focused and systematicmanner. Second,it informspractitioners of the expectations of them thereby fostering professionalism. Third, it prepares the publicfor SIAs by elucidating the functions and values of the assessment.

© 2014 Elsevier Inc. All rights reserved.

Introduction

Social impact assessment (SIA) is a strategic tool for managing thesocial consequences of development. Through analysing and monitor-ing the social change processes and social impacts of planned interven-tions, it fosters the sustainability and equitability of the biophysical andhuman environment (Vanclay, 2003). For its value in promoting cost-effectiveness in the long run, SIA has been applied to an array of arenassuch as dam construction (e.g. Wang et al., 2013), mining (e.g. Lockie,2009), land use management (e.g. Tilt et al., 2009), food control (e.g.Dreyer et al., 2010), agriculture (e.g. Bournaris andManos, 2012),fishery(e.g. Pollnac et al., 2006), sports (e.g. Burnett, 2001), transportation andprocurement (e.g. Esteves and Barclay, 2011), public management(Antonie, 2012), supply chain management (Esteves et al, 2012) anddisaster management (e.g. Kumagai et al., 2006).

Given thiswide application, the practitioners of SIA also come from awide spectrum of disciplines (Baines et al., 2013; Morgan et al., 2012).Practitioners, in this context, refer to the people who “practice themethodology of SIA and undertake associated social and environmentalresearch to inform the practice of SIA” (Vanclay, 2003; p. 2). Theyusually first have training in other professions, then learn and practiceSIA methodologies.

ue, Hawthorn, Victoria 3122,

Wong), [email protected]

Kowloon, Hong Kong Special

Corresponding to the purposes and context of SIAs, the types of prac-titioners vary. For example, in the SIAs conducted by corporations toseek social license for their development projects, the practitionerscan be the internal staff or external private consultants. In the commu-nity initiated SIAs, the practitioners can be the community members orconsultants hired from universities (Vanclay, 2003).

As SIA is a trans-disciplinary social science which requires knowl-edge ranging from sociology, anthropology, demography to environ-mental law (Esteves et al., 2012); the exercises usually employ a teamapproach so that each professional can contribute their expertise andmake the best use of inter-professionalism (Morgan et al., 2012;Vanclay, 2003).

While all SIAs are generally guided by the International Principles forSocial Impact Assessment (the Principles), each practice is case-specific(Vanclay, 2003). The selection of study scope and targets, the adaptionsof methods, and the formulation of plans all demand a sensitive andflexible use of SIA theories and methods. Hence, the quality of SIAs islargely, though not solely, determined by the ethics and capabilities ofthe practitioners.

Literature shows how the inadequacies and malpractices of practi-tioners hamper the effectiveness of SIAs. For example, Suopajärvi(2013) reported that by failing to perform a thorough scoping, the prac-titioners resulted in leaving some vulnerable groups in the impact areasunassessed. Burdge and Johnson (1994) revealed that some practi-tioners refused to conduct primary research for saving cost and time;hence their research lacked empirical evidence. Harvey et al. (2011)also called for attention to the misconduct of deliberately shapinga favourable public opinion by controlling the content, structure andorganisation of public engagement. Goldenberg and Frideres (1986)

Records identified in Scopus(n = 75)

Records identified in ScienceDirect

(n = 333)

Papers from Key Citations(n = 27)

Papers after removal of

duplicates and non-English paper

(n = 413)

Papers screened(n = 362)

Removal of abstracts, book

reviews, editorials and other supporting materials(n =51)

Full-text articles for eligibility

assessment(n = 374)

Papers identified from

cross-referencing(n = 12)

Studies included in thematic analysis

(n = 73)

Papers not discussed SIA

practices excluded(n = 270)

Papers lacked generalizability

excluded(n = 31)

Identification

Screening

Selection

Fig. 1. Data selection flow chart.

125C.H.M. Wong, W. Ho / Environmental Impact Assessment Review 50 (2015) 124–133

pointed out that many public participation programmes organised inSIAs were only delivering information but failed to solicit inputs fromcommunities.

Despite the gatekeeper role of SIA practitioners, limited literature fo-cuses on the expectations for them.We used “social impact assessment”and “practitioner” as the search keys in Scopus and ScienceDirectJournals, the two databases which store a substantial amount ofenvironmental science literature, in the early July 2014, and found nojournal or book that used them in title. Recently, with the publishingof the two papers on ethical practices (Baines et al., 2013; Vanclayet al., 2013), more light has been shed on the practitioners. However,to our knowledge, there has still been no research on the expectedroles of the professionals. Seeing this knowledge gap, we employedthe systematic review technique to collect related propositions andevidence scattered in the literature to construct a framework of rolesof SIA practitioners.

The significance of this research is threefold: It is a pioneer study tosystematically investigate the roles of SIA practitioners; it informs theexisting and prospective practitioners of the expectations on themthereby reinforcing professionalism; it prepares the public, especiallythose involved in the assessments, of what to anticipate thus settinga context for collaboration. The rest of this paper is structured intofour sections: methodology, conceptual framework, limitations andsuggestions, and conclusion.

Methodology

Guiding references

This research was guided by two references — the PreferredReporting Items for Systemic Reviews and Meta-Analyses (PRISMA)(Liberati et al., 2009; Moher et al., 2009) and a paper using reviewmethod to identify roles of librarians (Cooper and Crum, 2013). PRISMAis an evidence-based guide for reporting systemic reviews and meta-analyses. It contains a list of 27 items to be included in the researchwrit-ing and a flowchart portraying the data selection process. Although it isoriginally designed for synthesising the clinical results of randomisedtrials, it can also be adapted for other types of research (Liberati et al.,2009; Moher et al., 2009). This reference provides a practical and com-prehensive roadmap for our data collection and selection.

“New activities and changing roles of health sciences librarians: asystemic review, 1990–2012”, our second research method reference,is an example demonstrating a different use of PRISMA. In it, Cooperand Crum (2013) followed the steps instructed to reduce 371 papersin their preliminary search to a manageable amount of 50 articles foranalysis. This reference exemplified the application of PRISMA to roleidentification.

Data search and selection

We recognise that SIA practitioner per se is already a role; hence,what we actually explored in this study were the sub-roles (Hoffman,1959). Just as the counsellors who serve the racial/ethnic minoritieshave eight sub-roles as adviser, consultant, counsellor, change agent,psychotherapist, facilitator of indigenous healing methods, advocate,and facilitator of indigenous support system (Atkinson et al., 1993);we see that the SIA practitioners also have their sub-roles which de-scribe the multiple dimensions of their work.

However, unlike the well-established field of counselling and librar-ianship, the literature rarely examines the job as a SIA practitioner; thus,the use of search keys such as “role”, “job” and “position”, as in Cooperand Crum's paper (2013), did not yield useful results. We resolved thisproblem by loosening our criteria to include two key phrases — “socialimpact assessment” AND “practitioner”.

Our search was performed in “all fields” with the use of Scopus andScienceDirect Journals databases in the early July 2014. Limitation was

set to “peer-reviewed journals”. In the initial search, 75 papers werelocated in Scopus and 333 in ScienceDirect Journals. Both conceptualand research report papers were retrieved. One non-English paperwas removed. We then added 27 papers listed on the key citation listof SIA provided by the International Association for Impact Assessment(IAIA, 2009). Among these 434 papers, 21 duplicates were identifiedand removed. A filtering was conducted to exclude all abstracts, bookreviews, editorials, and other supporting materials, leaving 362 papers.

We then proceeded to content assessment for eligibility. The inclu-sion criteria were: papers that (1) concerned SIAs or impact assessmentin general, and (2) discussed the goals, quality or work of practitioners.We excluded papers that (1) dedicated to other types of impact assess-ments such as health impact assessment (HIA), environmental impactassessment (EIA) and strategic environment assessment (SEA), or(2) examined the applications of SIAs in a specific contextwithout offer-ing insights for general practice. Twelve additional papers were foundfrom cross-referencing in the selection process. Altogether, we assessed374 articles, and identified 73 relevant ones. Fig. 1 illuminates our dataselection process. Of these 73 records, 64 focused on SIAs and 9 dis-cussed more than one type of impact assessments (Fig. 2). Thirty four(46.6%) of them were from Environmental Impact Assessment Review,19 (26%) from Impact Assessment and Project Appraisal, and 20(27.4%) from other journals (Fig. 3).

Data analysis and conceptualisation of framework

To identify the roles of SIA practitioners from the selected literature,we adopted thematic analysis due to its usefulness in coding new ideas.It places an accent on what is “in” the data, and allows themes toemerge. The conceptualisation process is inductive, and no prede-termined codes are used. Researchers unfold the analysis throughthree procedures — open, axial and selective coding; and graduallyconstruct an organised view from observation (Ezzy, 2002; Straussand Corbin, 1990). Although this methodology is devised for processingprimary qualitative data; we found it suitable for analysing our second-ary data. Fig. 4 portrays the procedures in our data analysis.

9, 12%

64, 88%

Impact assessmentsSIAs

Fig. 2. Focuses of selected articles.

Fig. 4. Data analysis and framework conceptualisation flow chart.

126 C.H.M. Wong, W. Ho / Environmental Impact Assessment Review 50 (2015) 124–133

WeusedNVivio10 to assist coding. In the open coding stage,we codeddata in-vivo or with a descriptive label. These codes were experimentalthat served to group data for comparison. Throughout this process, wecontinued to add new codes, rename the existing ones, introducesecond-level codes and recode until data saturation. The evolvementwas stimulated by constant comparison and re-examination of articles.

After coding the 73 papers, we moved on to the axial coding stage.We examined the associations between codes and integrated theminto different expectations. To enhance content validity and reliability,wematched these themes back to our dataset and confirmed 11 expec-tations. In the selective coding stage, we identified a core role of a prac-titioner from each expectation, and stratified the roles into threecategories to build a structure into the framework.

Research findings: conceptual framework of roles of SIA practitioners

In our conceptual framework, we categorise the roles of SIA practi-tioners into three groups — project, community and SIA development.Under these umbrellas, there are eleven roles, namely project managerof SIA, practitioner of SIA methodologies, social researcher, social strat-egy developer, social impact management consultant, communitydeveloper, visionary, public involvement specialist, coordinator, SIAresearcher, and educator. Fig. 5 depicts our conceptual framework andTable 1 summarises the definition of each role.

Sociological Inquiry

Rural Sociology

Resources Policy

Ocean & Costal Management

Journal of Environmental Assessment Policy…

Futures

European Journal of Operational Research

Environment and Behavior

Ethics, Place and Environment

Diversity and Distribution

Annual Review of Sociology

Human Organization

Society and Natural Resources

Impact Assessment

Impact Assessment and Project Appraisal

Environmental Impact Assessment Review

0 5 10 15 20 25 30 35 40

Fig. 3. Distribution of selected data across journals.

Roles in project development

Planned interventions can take the form of projects, plans, pro-grammes and policies (Vanclay, 2003, 2012; Wolf, 1980). Despite thisdifferentiation, we found that the use of “project” to denote all formsof planned intervention prevailed (e.g. Becker et al., 2003; Buchan,2003; Mahmoudi et al., 2013; Ross and McGee, 2006).

Meanwhile, some scholars also referred SIAs themselves as projects(e.g. Becker, 2003; Rowan and Streather, 2011), though this usage hasnot been prevalent. From our observation, SIAs do possess whatmakes a project; that is (1) they are temporary; (2) they have a clearstart and end date; and (3) they involve a product or service productionprocess to create somethingnew(HeldmanandMangano, 2011). Clearlypositioning SIAs as projects, we believe, brings two advantages. First, itoffers a clear project structure to guide the development of SIAs fromthe initial phase to the closing. Second, it paves way for tapping intothe rich resources of project management tools to enhance the SIApractices.

Fig. 5. Framework of roles of SIA practitioners.

Table 1Definitions of roles of SIA practitioners.

Roles of SIA practitioners

Project developmentSIA project manager- People who are responsible for managing the SIA processes and applying

tools and techniques to carry out SIA activities.Practitioner of SIA methodologies- People who apply SIA methodologies with discernment and flexibility.

Social researcher- People undertake SIA research and apply social theories and concepts to

all research processes.Social strategy developer- People who devise mitigation, coping and enhancement strategies for

planned interventions based on the findings of predictive assessment.Social impact management consultant- People who participate in the implementation of planned intervention

as a consultant to manage the social impacts of the project.Community developmentCommunity developer- People who contribute to the sustainability and betterment of community.

Visionary- People who envisage the future development of community and

extrapolate the impact pathways of the planned interventions.Public involvement specialist- People who deliberately seek communities' involvement in the planning,

implementation and evaluation of the planned interventions.Coordinator- People who facilitate discussion and negotiation among different

parties involved in the planned interventions.SIA developmentSIA researcher- People who conduct SIA research and share the learning with other

practitioners for the purpose of improving SIA practices.Educator- People who educate others about the core concepts of SIA and inculcate

the SIA values into the practice norm.

127C.H.M. Wong, W. Ho / Environmental Impact Assessment Review 50 (2015) 124–133

In our conceptualisation, we recognise both SIAs and the plannedinterventions as projects. To avoid confusion, we always give a contextto the usage. An example of it is the “SIA project manager”.

For roles in project development, we have five propositions: projectmanager of SIA, practitioner of SIA methodologies, social researcher,social strategy developer, and social impact management consultant.

Role 1: project manager of SIAWhen SIAs are seen as projects, then logically, SIA practitioners

assumed the role to manage these projects. Adapting the definition ofproject managers provided by Heldman and Mangano (2011), the SIAproject managers are responsible for managing the SIA processes andapplying tools and techniques to carry out the SIA activities.

SIAs progress in five phases in a project life cycle — the initiating,planning, executing, monitoring and closing phases. Revealed in ouranalysis was a lack of exploration of SIA activities in the initiating andclosing phases. This may be explained by a call for developing andimproving the SIA methodologies (Rowan, 2009; Schirmer, 2011;Vanclay, 2004) that drew attention to the planning to monitoringphases.

Desirably, all SIAs can span across the planning and implementationof the planned interventions; however, given the tight financial andtime budgets, some of them can only contribute to the planning.Acknowledging this, we examined the project life cycles of SIAs inboth circumstances. The following is an illustration with SIA activitieslargely drawn from the Social Impact Management Plan (SIMP) (Franksand Vanclay, 2013) (Fig. 6). Although they are by no means exhaustive,they serve well to give directions of the types of SIA processes in eachproject phase.

SIA commences when the developers of planned interventions,community members or other proponents decide to conduct a SIA.In the initiating stage, a SIA team is set up to plan and manage thewhole SIA cycle. There are two sets of planning questions they have to

consider — (1) the criterion problem that defines the goals and perfor-mance; and (2) the analytic problem that concerns the design ofmethods (Wolf, 1980). When these parameters are ready, the nextstep is to prepare for the predictive assessment. Activities here includescoping, formulating intervention alternatives, profiling and conductingbaseline studies. In the executing stage, SIA practitioners assess theprobable social consequences of different alternatives. The findings areused to inform the design and selection of intervention, and formulatesocial management strategies in the monitoring stage. In the closingstage, the project manager reports the assessment processes and find-ings to the proponents, and shares the information with the publicand SIA community.

For the SIAs that continue to the implementation of interventions,the SIA project managers are accountable for tracking the developmentof social impacts and advising any necessarymeasures. At the end of theimplementation, the SIAs close with a post-intervention evaluation toreview the effectiveness of each process as well as the overall perfor-mance. The experience has to be documented for future reference andshared with communities and other practitioners.

An effective impact assessment has to meet several criteria (Bondet al., 2013; Chanchitpricha and Bond, 2013): First, it works. Second, itfulfils all its objectives. Third, it informs the decision making of theinterventions. Fourth, it gains acceptance from the key stakeholders.Fifth, it facilitates the learning of stakeholders and improves theirviews. To achieve these goals, SIA project managers have to be com-petent in (1) attaining project goals, (2) defining business cases,(3) formulating and implementing appropriate strategies in a timelymanner, (4) soliciting strong support from stakeholders, (5) obtainingsufficient funds and resources, (6) managing people, risks and changes,(7) technical capability, (8) cultivating effective organisational cultureand structure, (9) being sensitive to the health and safety needs, and(10) communication (Lock, 2013).

Role 2: practitioner of SIA methodologiesPractitioners are expected to apply the SIA methodologies with

discernment and flexibility (Burdge, 1990; Vanclay, 2003). To do so,they need to acquire the knowledge of SIA theories andmethods, collecta stock of SIA tools, accumulate practical experiences, and developinsights from case studies (Esteves et al., 2012).

Following the advancement of the field, more resources becomeavailable. Concerning the theories and conceptual frameworks, thereare Burdge's (1987) SIA model, community empowerment framework(Gagnon et al., 1993), community response model (Blishen et al.,1979; Bowles, 1981; Ross andMcGee, 2006), community organisationalmodel (Little and Krannich, 1988; Ross andMcGee, 2006), social organi-sation model (Branch et al., 1984; Ross and McGee, 2006), SIA in thepolicy process (Dietz, 1987), and temporal phases and affected systemsframework (Gramling and Freudenburg, 1992). For models that amal-gamated with other professions, there are conflict-sensitive impactassessment (Kapelus et al., 2011), functional evaluation (Slootweget al., 2001), and risk and social impact assessment (Mahmoudi et al.,2013). Regarding the tools, there are sensitivity analysis (Wolf, 1983),scenario simulations (Becker, 2001), multi-criteria decision makinganalysis (MCDA; Estévez et al., 2013), social development needs analy-sis (Esteves and Vanclay, 2009) and SIMPs (Franks and Vanclay, 2013).Furthermore, myriads of SIAs have been conducted in different fieldsand in different regions for case study (e.g. du Pisani and Sandham,2006; Henry, 1990; Holm et al., 2013; Ip, 1990; O'Faircheallaigh, 2009;Suopajärvi, 2013; Tang et al., 2008).

Despite the effort, the selection, application and reporting of SIAmethods remain a weakness. The chosen methods have been foundlacking reliability, validity, robustness and significance levels (Burdgeand Vanclay, 1996; Esteves et al., 2012). When applying the methods,some practitioners failed to consider the alternatives, collect the qualitybaseline data, involve the public in a meaningful way, assess the cumu-lative impacts, and identify the distribution of impacts and benefits

Fig. 6. SIA activities in a project life cycle.

128 C.H.M. Wong, W. Ho / Environmental Impact Assessment Review 50 (2015) 124–133

(Esteves et al., 2012; Pope et al., 2013). Many practitioners did notreport their methods, sources and assumptions (Burdge and Vanclay,1996; Esteves et al., 2012). In the face of these problems, it is especiallyimportant to make known of the SIA methodologies practitioner role.Some good practices are documented in Esteves et al. (2012) andVanclay (2012).

Role 3: social researcherAs SIA is a research and a paradigm of social sciences (Esteves et al.,

2012; Finsterbusch, 1985; Vanclay, 2003;Wolf, 1982), therefore the SIApractitioners are social researchers. In this role, practitioners are expect-ed to apply social theories and concepts to all SIA activities (Baines et al.,2013; Burdge, 1990, 2003; Chase, 1990; du Pisani and Sandham, 2006;Interorganizational Committee on Guidelines and Principles for SocialImpact Assessment, 1994; Ross and McGee, 2006; Rowan and Streather,2011; Sairinen and Kumpulainen, 2006; Vanclay, 2003; Vanclay andEsteves, 2011; Vanclay et al., 2013).

As a social researcher, the practitioners have to:

● Understand the social dynamics of impacted communities;● Determine the research scope and subjects with the knowledge of

social organisation;● Develop the conceptual frameworkwith reference to social theories;● Adhere to the SIA principles and research ethics● Prepare social impact variables;● Collect primary and secondary data with social investigation

techniques;● Assess the primary, secondary and cumulative social impacts of

planned interventions in different development stages;

● Interpret the linkages between social variables;● Assist the choosing and designing of intervention alternatives

with findings from social research;● Devise measures to manage positive and negative social conse-

quences; and● Inform the distribution of compensations and benefits.

The literature reviewed suggested some knowledgewhich is condu-cive to the SIA research. The key concepts include power, culture, partic-ipation, difference, community, human rights, gender, justice, place,resilience, sustainable livelihood, capital and participatory approach(Esteves et al., 2012; Howitt, 2011; Ross and McGee, 2006). Amongthe disciplines in social sciences, sociology and community develop-ment have found to be the most useful for locating social receptorsand community resources in the baseline studies (Rowan, 2009).The use of social capital, especially the partnership with local com-munities, is essential for developing enhancement measures (Rowanand Streather, 2011). Lists of social changes processes and social impactvariables are composed for consideration (e.g. Cloquell-Ballester et al.,2006; Vanclay, 2002).

The application of theories and concepts can be challenging (Burdgeand Vanclay, 1996; Vanclay, 2004). The propositions and the uses oflanguage in different social sciences disciplines are sometimes contra-dictory. Not all social sciences theories can provide practical and proac-tive recommendations. The qualitative data requires value-weightingwhich inevitability introduces subjectivity. To these difficulties, we pro-pose four mitigations:

First is the use of triangulation to enhance validity. Esteves andVanclay (2009) recommended using four data collection methods

129C.H.M. Wong, W. Ho / Environmental Impact Assessment Review 50 (2015) 124–133

simultaneously — soliciting local residents' perspectives with qualita-tive and quantitation techniques, analysing impacts with the use ofquantitative indicators, combining primary and secondary data sources,and including expert judgments from experienced SIA practitioners.

Second is the employment of creditability controls for qualitativeanalyses. For instance, Creswell and Miller (2000) examined the use ofnine validity procedures, namely triangulation, member checking, theaudit trail, disconfirming evidence, prolonged engagement in the field,thick and rich description, researcher reflexivity, collaboration, andpeer debriefing. Patton (2002), on the other hand, suggested five setsof evaluation criteria — traditional scientific research criteria, socialconstruction and constructivist criteria, artistic and evocative criteria,critical change criteria and evaluation standards and principles.

Third is using SIAs only for the purpose they are designed for, that isto manage process (Craig, 1990; Finsterbusch, 1995; Vanclay, 2004).Practitioners and decisionmakers are not advised to base their decisionson the face value of the assessment results; rather, they should considerthe impact pathways articulated andmake flexible plans to prevent andaddress the probable consequences.

Fourth is the sharing of learning with other practitioners. IAIA hashoused the practitioners and encourages exchanges among them. Mean-while, journals, especially the Environmental Impact Assessment Reviewand Impact Assessment and Project Appraisal, have published manyconceptual and research papers which facilitate knowledge transfer.

Role 4: social strategy developerSIAs have been recognised as a tool to devise social management

plans for the planned interventions based on the findings of predictiveassessment since its inception (Freudenburg, 1986; Wolf, 1974, 1983);hence SIA practitioners have a role as a social strategy developer.

Summarised from our data were four goals of social strategies. First,they must seek to maximise the benefits for stakeholders and minimisethe negative consequences (Vanclay, 2003). Second, if possible, theyshould turn risks into benefits (Rowan and Streather, 2011; Vanclay,2006). Third, they have to contribute to the betterment of communities(Vanclay, 2003). Fourth, they need to assist proponents to achieve theirobjectives (Loxton et al., 2013). While scholars appeared to arrive at aconsensus on the first three goals, the fourth one remains controversial.Wolf (1983) advocated that SIAs should not just be a tactic for obtainingsocial license but an instrument to consider different interventionoptions, including the no intervention option which may contradictthe will of proponent.

SIA practitioners conceive three types of social strategies:mitigation,coping and enhancement measures. Mitigation measures are abouteliminating or alleviating the negative impacts arisen from the interven-tion; coping strategies deal with the unavoidable negative impactswhich the stakeholders need to accept and tolerate; enhancementplans concern bringing out benefits to the communities (e.g. Baineset al., 2013; João et al., 2011; Loxton et al., 2011; Rowan and Streather,2011; Vanclay, 2003). When formulating these strategies, the SIA prac-titioners need to take the following into consideration:

(1) Corporate social responsibility (ISO, 2010; Rowan and Streather,2011)

(2) Community development (João et al., 2011; Vanclay, 2003)(3) Different levels of strategies — individual, family, business and

community (Loxton et al., 2011)(4) Local specificity (Baines et al., 2013; Esteves, 2008; Vanclay,

2003)(5) Distribution of benefits (Vanclay, 2003)(6) Duration of measures (Loxton et al., 2013)(7) Avoidance of over-promise (Vanclay, 2012)(8) Hierarchy of control/mitigation hierarchy — first seek to avoid,

mitigate and minimise the negative impacts, then consider com-pensation and benefit sharing (Holm et al., 2013; João et al.,2011).

(9) Enhancement hierarchy— enhance the positive effects of project,then go beyond to enhance thewellbeing of local area andwiderarea (João et al., 2011).

Role 5: social impact management consultantSIAs aremostmeaningfulwhen the strategy proposals are translated

into actions (Égré, and Senécal, 2003; O'Faircheallaigh, 2009). As men-tioned in the section Role 1: project manager of SIA, some practitionersparticipate in the implementation of interventionwith a role tomanagethe social impacts.

The tool, SIMP, is devised especially for carrying out this role. Itserves to signpost the priorities, resources, strategies, processes, activi-ties, commitments and staffing of the measures (Franks and Vanclay,2013); hence, it assists the project stakeholders to identify their rolesand responsibilities in a larger project scope and engender their man-agement plans for the intervention (Esteves et al., 2012; Holm et al.,2013; Interorganizational Committee on Principles and Guidelines forSocial Impact Assessment, 2003). FromHolm et al.'s (2013) perspective,it is best to utilise the results of predictive assessment to developthe plans. The implementation of strategies can be made through thedevelopment of management system, impact and benefit agreements,social programmes, and standard operating procedures (Franks andVanclay, 2013).

The role of a social impact management consultant does not stopwhen the social strategies are introduced. Throughout the developmentprojects, SIA practitioners have to monitor the use of the SIMPs and en-vironmental management plans, manage anxiety and conflicts, identifydiscrepancies between the predicted and actual social impacts, reportthe changes to stakeholders, and propose measures to promote benefitto cost efficiency (Barrow, 2010; Franks and Vanclay, 2013; Rossouwand Malan, 2007; Vanclay, 2012). Ideally, this monitoring role is to beperformed in collaboration with other community stakeholders(Armour, 1988; Franks and Vanclay, 2013).

As per our analysis, the success of social strategies hinges on an inte-gration of strategies into policies, an adaptive management and aneffective communication (Boggs, 1994; Burdge and Vanclay, 1998; Dareet al., 2011a; Loxton et al., 2013; Sairinen and Kumpulainen, 2006;Vanclay, 2012). The community members need to be informed of theirrights and obligations as well as the details of the different measures. Toensure that the messages reach different social groups, SIA practitionersneed to employ multiple communication approaches and use them in away that matches the stakeholders' preferred modes. The informationhas to be transparent, accessible and clear (Loxton et al., 2013).

Roles in community development

The recognition of social diversity leads us to the discussion of com-munity. Whereas its members share a community identity; they are,at the same time, embedded into different social groups and possessdifferent characteristics (Vanclay, 2012). For a well-thought SIA, it hasto consider the concerns of each group, examine the distribution ofimpacts, and devise specific strategies accordingly (InterorganizationalCommittee on Guidelines and Principles for Social Impact Assessment,1994; Vanclay, 2003). In addition to meeting the needs of stakeholders,SIA practitioners are encouraged to take the larger community intoconsideration (Esteves and Vanclay, 2009), especially when the second-ary and higher ordered social impacts usually cause more damages(Vanclay, 2012).

In our conceptual framework, the roles of SIA practitioners incommunity development are (1) community developer, (2) visionary,(3) public involvement specialist, and (4) coordinator.

Role 6: community developerUnderscored in the Principles (Vanclay, 2003), SIAs have to contrib-

ute to the sustainability and betterment of community, therefore thepractitioners should see themselves as a community developer. In the

130 C.H.M. Wong, W. Ho / Environmental Impact Assessment Review 50 (2015) 124–133

design of intervention alternatives and social strategies, practitionersneed to aim at engendering long-lasting positive outcomes (Franks andVanclay, 2013; João et al., 2011; Vanclay, 2003; Vanclay and Esteves,2011). Below are some community development goals exemplified inthe literature (e.g. Rowan and Streather, 2011; Vanclay, 2003, 2012):

● Protect tangible and intangible cultural heritage;● Cultivate community and individual capacities;● Empower local people;● Develop social capital;● Enhance the position of disadvantaged or marginalised members

of society;● Abate dependency;● Promote equity;● Reduce poverty; and● Create employment opportunities.

Role 7: visionaryThe role of a community developer cannot be performedwithout the

SIA practitioners being a visionary. To build a better future, one has tofirst envisage the possible transformation of the community at an intu-itive level, and foresee the necessary resources and procedures toactualise the visions. On the other hand, SIAs as predict exercises alsodemand the same abstract thinking to forecast the social change pro-cesses and social impacts of planned interventions.

The looking-into-the-future in both cases, however, does not devel-op in vacuum. The extrapolation has to be devised from studying similarcases (e.g. Burdge, 1987), conducting scenario testing (Becker, 2001;João et al., 2011) and backcasting (Robinson, 2003; Vanclay, 2012),soliciting ideas from locals (e.g. Dale and Lane, 2008; Vanclay, 2003,2012), and applying planning techniques (João et al., 2011; Vanclay,2012). As observed in the data, few SIA papers have exploited the plan-ning theories. To this, we suggest gaining insights from Lawrence(2000)'s paper on the planning theories and environmental impactassessment.

Role 8: public involvement specialistRepeatedly mentioned in this paper is the use of participatory ap-

proach to seek communities' inputs to the SIA processes (e.g. Beckeret al., 2004; Burdge and Robertson, 1990; Dare et al., 2011a; Esteveset al., 2012; Franks and Vanclay, 2013; Lockie, 2007; Vanclay, 2003,2012). It is an endeavour to incorporate local knowledge into the plan-ning and decision making so that the interventions can bring mutualbenefits to the involved parties (e.g. Esteves et al., 2012; Lockie, 2001;Vanclay, 2003). Besides encouraging stakeholders to voice out; whereappropriate, the practitioners can also invite them to lead in certainplanning and reviewing activities (Franks and Vanclay, 2013). As aneffective public involvement needs professional skills and experience(Vanclay, 2012), SIA practitioners have to be a specialist.

There are several fundamental public involvement concepts that thepractitioners need to grasp firmly. First is diversity. It has been exploredin the section Roles in community development of this article. Second isstakeholder. Defined by Dare et al. (2011b), the stakeholders of aplanned intervention not only include the affected parties, but also thepeople who are interested or are influential. Third is deliberation. Thepractitioners are expected to take “deliberate” effort to reach the stake-holders, especially those worst-off society members who often keepsilence in the engagement process and barely have resources to defendtheir rights (Vanclay, 2012). [Hartz-Karp and Pope (2011) expoundedon deliberative democracy.] Fourth is the free, prior and informedconsent which is achieved when the social researchers uphold theirethics (Esteves et al., 2012; Hanna and Vanclay, 2013; Howitt, 2005).

While scholars generally recognise the values of participatory SIA, itis proposed that the integration of it with the technocratic approachwillresult in an even better outcome (Becker et al., 2004; Gagnon et al.,1993; Lane et al., 1997;Manring et al., 1990). The technocratic approach

is about the use of expert knowledgewhich complements theweaknessof participatory approach.

A successful public involvement attains multiple outcomes (Baineset al., 2013; Buchan, 2003; Esteves, 2008; Karjalainen and Järvikoski,2010; Sairinen et al., 2010; Vanclay, 2003, 2012):

● It allows communities to air their grievance, anger and hope, andleads to anxiety reduction, healing and coping;

● It renders the perceptions of fairness and builds trust;● It facilitates discussion thereby assisting consensus building and

conflict resolution;● It brings social objectives into light thus fostering community's

ownership of the decisions;● It helps obtain social license for development and reinforces its

sustainability; and● It cultivates human and community capitals.

Nevertheless, when mismanaged, public involvement can bringharm to the current and future SIAs. The engagement sometimes intro-duces redundant or controversial informationwhichmay ignite conflict(Becker et al., 2004; Manring et al, 1990). If this happens, practitionershave to show their impartiality and reliability so as to regain the trust(Prenzel and Vanclay, 2014). A prolonged social involvement, on theother hand, drains the enthusiasm of community members and causesconsultation fatigue. To prevent this from happening, SIA practitionersneed to be transparentwith the time pressure they are facing, negotiatethe meeting arrangements in advance, make an effort to meet at placesconvenient to the informers, show their willingness to engage, and pro-vide prompt feedback (Baines et al., 2013). Vanclay (2012) reminded usthat a sincere andwell-thought engagement alleviates fear and anxiety.A lack of genuine concern and a dismissive attitude towards opposition,however, generate distrust and scepticism.

Role 9: coordinatorThe SIA practitioners do not work on their own but in partnership

with other stakeholders such as the government agencies, project pro-ponents and communities. In the cooperation, the SIA practitionerstake up a coordinator role to bridge the different parties, and facilitateconversations and negotiations (Égré, and Senécal, 2003; Esteves et al.,2012; Franks and Vanclay, 2013; O'Faircheallaigh, 1999; Vanclay,2012). This mediation work is underscored in the SIMPs (Franks andVanclay, 2013).

For the building of consensus among stakeholders, there are toolssuch as cooperative discourse (Webler et al., 1995), interactive commu-nity forum (ICF; Becker et al., 2003), MCDA (Estévez et al., 2013) andstrategic perspectives (Dale and Lane, 2008).

Roles in SIA development

In addition to the roles in project and community development, theSIA practitioners are also responsible for the advancement of SIA. In thisarena, we have conceptualised two roles— SIA researcher and educator.

Role 10: SIA researcherThe practices of SIA are grounded on the SIA methodologies devel-

oped through research around the globe (Vanclay, 2003). Thus, the con-tinuous advancement of the field heavily relies on the global endeavourto undertake social and environmental research and share the learnings(Vanclay, 2003). This collaboration is recognised as one of the strengthsof impact assessments by Pope et al. (2013).

Role 11: educatorSIA practitioners are called to promote the values of SIA by teaching

them to the others and inculcate them into the practice norm. Esteveset al. (2012) saw it necessary to educate the proponents, regulators,and impact assessment colleagues from other professionals about the

131C.H.M. Wong, W. Ho / Environmental Impact Assessment Review 50 (2015) 124–133

core concepts in SIA paradigm. By doing so, the practitioners can gainthe acceptance and recognition from the public.

Interrelatedness of roles

To facilitate readers to understand the eleven sub-roles of SIA prac-titioners, we have labelled them under three categorises. Indeed, allthese roles are interrelated and should be examined together. Wehave used two-sided arrows to indicate the connectedness in Fig. 5.Here we exemplify the intra- and inter-group relationships.

Examples of intra-group connectedness:

● The competitiveness of project managers is demonstrated in theireffective development and management of social strategies.

● Tobe an effective coordinator betweenproponent and communities,one has to be competent in public involvement so as to solicit thepublic's participation.

Examples of inter-group connectedness:

● An effective public involvement requires the social inquiry tech-niques of a social researcher.

● When adopting the participatory approach of SIA, practitioners needto seek communities' inputs in the development, monitoring andevaluation of social strategies.

Limitations and suggestions for future research

Despite our best effort, this research still entails some limitations.First, to select and arrange data for the conceptualisation of framework,we inevitably applied abstraction for inductive analysis and instilledsubjectivity. Noticing the potential biases, we tried to enhance thecontent validity by re-examining all the roles with the data. Second,although we seek to include a comprehensive dataset for derivingmeaningful analyses, we cannotmake a claim of including all data avail-able due to a constraint of manpower. However, the saturation in anal-ysis reflected an adequate coverage. Third, as we selected only thepapers that inform the general practice of SIAs, our framework willnot be adequate to cover all roles in every field. As to the limitationsof this review, we urge researchers to undertake qualitative and quanti-tative studies to examine the roles proposed, especially for specific dis-cipline. Also, as our analysis revealed a lack of studies on the initiatingand closing phases of SIAs, we recommend exploration in these twoareas. More, the selection, application and reporting of SIAs appearto be a continuous challenge, hence we suggest more proposals ofimprovement. Lastly, we encourage more studies on the utilisation ofplanning resources to support the performing of visionary role.

Conclusion

Recognising the lack of deliberate discussions on the expectationsfor SIA practitioners, we employed the systematic review approach toconstruct a framework of roles of practitioners. From the literature, weidentified eleven roles and divided them into three categories — rolesin project, community, and SIA development. For project development,the propositions include project manager of SIA, practitioner of SIAmethodologies, social researcher, social strategy developer, and socialimpact management consultant. For community development, we pro-pose the roles of community developer, visionary, public involvementspecialist, and coordinator. For the development of SIA community,there are SIA researcher, and educator. Despite the categorisation,all roles are indeed interrelated. This study is significant in three ways.First, it pioneers to study the roles of SIA practitioners in a focused andsystematic manner. Second, it informs the practitioners of the expecta-tions for them thereby fostering professionalism. Third, it preparesthe public for SIAs by elucidating the functions and values of theassessment.

Acknowledgements

The idea of this study was conceived when we undertook the SocialImpactAssessment of UrbanRenewal Plan inKowloon City (Grant num-ber: PLNQ 4/2012), hence we acknowledge the District Urban RenewalForum for funding the project. For the conceptualisation of framework,we are indebted to Prof CHEUNG Chau Kiu Jacky, Prof CHAN HengChoon Oliver, Prof CHEUNG Sing Hang andMr Cyrus Leung for their ad-vices. A special thank is given to Prof Andreas Hirschi who generouslyshared his experience and reading in theory building. We also thankthe anonymous reviewers for their constructive comments.

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CeciliaWongholds a BBA inHumanResourcesManagementand aMaster's degree of Social Sciences in Counselling. She isdedicated to multidisciplinary research with interests inassessment and evaluation, community development, careerdevelopment and social relationships. Before her career in

academia, she practiced as a human resource and trainingconsultant in Hong Kong, Mainland China and Macau.

Dr. Wing-Chung is Associate professor of sociology at CityUniversity of Hong Kong and holds a PhD in anthropologyfrom SOAS, University of London. He has published broadlyon community studies and social problems in relation to sub-ordinate people in Hong Kong and Chinese societies. His aca-demic articles appear in Journal of Contemporary Ethnography,Journal of Contemporary Asia, Modern Asian Studies, Journal ofSocial History and The Asia Pacific Journal of Anthropology. Heteaches mainly on social research issues and methods.