Hostname: page-component-cd9895bd7-gbm5v Total loading time: 0 Render date: 2024-12-23T04:52:16.311Z Has data issue: false hasContentIssue false

Social impact evaluation analysis: a systematic qualitative method for assessing engineered products

Published online by Cambridge University Press:  11 December 2024

Andrew G. Armstrong
Affiliation:
Department of Mechanical Engineering, Brigham Young University, Provo, UT, USA
Christopher A. Mattson*
Affiliation:
Department of Mechanical Engineering, Brigham Young University, Provo, UT, USA
John L. Salmon
Affiliation:
Department of Mechanical Engineering, Brigham Young University, Provo, UT, USA
Eric C. Dahlin
Affiliation:
Department of Sociology, Brigham Young University, Provo, UT, USA
Thomas B. Geilman
Affiliation:
Department of Mechanical Engineering, Brigham Young University, Provo, UT, USA
*
Corresponding author Christopher A. Mattson [email protected]
Rights & Permissions [Opens in a new window]

Abstract

Social impact has been widely discussed by the engineering community, but studies show that there is currently little systematic consideration of the social impact of products in both academia and in industry beyond social impacts on health and safety. While Failure Mode and Effect Analysis (FMEA) is useful for evaluating health and safety risks, new developments are needed to create an FMEA-style evaluation that can be applied to a wide range of social impacts for engineered products. The authors describe necessary modifications to traditional FMEA that transform it into a tool for social impact analysis. The modification of FMEA involves the introduction of positive and negative impacts, the inclusion of discrete and continuous impacts, the consideration of various stakeholder types, and the inclusion of uncertainty in place of detectability. This modified FMEA is referred to in this paper as Social Impact Effects Analysis (SIEA). The paper describes how SIEA is performed and articulates the potential benefits of SIEA.

Type
Research Article
Creative Commons
Creative Common License - CCCreative Common License - BY
This is an Open Access article, distributed under the terms of the Creative Commons Attribution licence (http://creativecommons.org/licenses/by/4.0), which permits unrestricted re-use, distribution and reproduction, provided the original article is properly cited.
Copyright
© The Author(s), 2024. Published by Cambridge University Press

1. Introduction

Sustainable design encapsulates economic, environmental, and social sustainability. Economic considerations are routinely included in engineering design (Asiedu and Gu, Reference Asiedu and Gu1998), and environmental considerations are increasingly being considered in design with standards and widely used methodology (Hendrickson et al., Reference Hendrickson, Horvath, Joshi and Lave1998; Joshi, Reference Joshi1999). While social impact considerations are being broadly researched (Phillips et al., Reference Phillips, Renda and McDonald2024; Hallstedt et al., Reference Hallstedt, Isaksson, Nylander, Andersson and Knuts2023; Udoewa, Reference Udoewa2022; Richards et al., Reference Richards, Stevenson, Mattson and Salmon2023), research reveals that there is a lack of implementation in engineering-centered academia and industry (Pack et al., Reference Pack, Rose Phipps, Mattson and Dahlin2020; Burleson et al., Reference Burleson, Sienko and Toyama2020).

The lack of implementation is not due to a lack of methods. There are many methodologies that are used in social science and global development fields, including 9 methodologies reviewed by Bonilla-Alicea and Fu (Bonilla-Alicea and Fu, Reference Bonilla-Alicea and Fu2019) and 18 reviewed by Burleson et al. (Burleson et al., Reference Burleson, Sienko and Toyama2020). Some reasons these methods are not widely used in engineering-centered product development are designers not being aware of methods, methods not being widely applicable, and methods being too complicated or time-consuming (Pack et al., Reference Pack, Rose Phipps, Mattson and Dahlin2020; Burleson et al., Reference Burleson, Sienko and Toyama2020).

In an intensive literature survey that encompassed multi-disciplinary publications, Rainock et al. categorized the impacts that engineered products can have on society into 11 social impact categories (Rainock et al., Reference Rainock, Everett, Pack, Dahlin and Mattson2018). Those categories are:

  1. i. Impacts on Conflict & Crime

  2. ii. Impacts on Cultural Heritage & Identity

  3. iii. Impacts on Education

  4. iv. Impacts on Family

  5. v. Impacts on Gender

  6. vi. Impacts on Health & Safety

  7. vii. Impacts on Human Rights

  8. viii. Impacts on Paid Work

  9. ix. Impacts on Population Change

  10. x. Impacts on Social Networks & Communication

  11. xi. Impacts on Stratification

Through a systematic review of industrial practice, Pack et. al found that Impacts on Health and Safety are the most widely considered/implemented in engineering practice and that Failure Mode and Effects Analysis (FMEA) is the predominant tool used by engineers for considering such impacts (Pack et al., Reference Pack, Rose Phipps, Mattson and Dahlin2020).

FMEA is a methodical, qualitative method for evaluating primarily the Health and Safety impacts of component failure in engineered systems (Mikulak et al., Reference Mikulak, McDermott and Beauregard2017). When carrying out an FMEA, designers methodically rate product components, their potential failure modes, and possible effects to determine risk associated with the product. As part of the FMEA process, designers list out many possible failure modes for each component in a system and rate each failure mode by its likelihood of occurrence. Designers then list out the negative effects for each failure mode and rate the severity of each effect. Designers also rate each failure mode on how easily each failure can be detected and prevented beforehand. The three ratings (occurrence, severity, and detectability) are used to calculate an overall risk priority number (RPN). The RPNs of each failure mode and effect are used to determine which failure modes need additional design, manufacturing, or quality control efforts to lower risk to acceptable levels.

FMEA was initially created by the United States Military as a means of managing risk and preventing future failures. Later, it was adopted by NASA in the 1960’s, the automotive industry in the 1970’s, and has since expanded in use to many industries, including the medical device industry, the construction industry, the consumer electronics industry, and so forth. Many of these, including the automotive and medical device industries, require the use of FMEA as part of meeting industry standards (Carlson, Reference Carlson2014; Mikulak et al., Reference Mikulak, McDermott and Beauregard2017).

Although FMEA has been widely used and generally accepted, few attempts have been made in archival journals to examine the validity of FMEA. The lack of archival research supporting FMEA, however, does not mean that FMEA is not an accepted and useful method (Shebl et al., Reference Shebl, Franklin and Barber2012; Breiing and Kunz, Reference Breiing and Kunz2002). FMEA has been validated by industry for decades and its consistent use demonstrates that FMEA is a valued, trusted method (Mikulak et al., Reference Mikulak, McDermott and Beauregard2017).

The simplicity, consistency, and ability to identify factors leading to failures and corresponding corrective actions early in the design process make FMEA popular (Stamatis, Reference Stamatis2003). FMEA is also valued because the risks identified by FMEA can be tracked through testing and post-product release as part of Quality Management Systems (QMS) and Risk Management Systems (Carbone and Tippett, Reference Carbone and Tippett2004; Dudek-Burlikowska, Reference Dudek-Burlikowska2011).

While FMEA is valuable for identifying failure modes and preventative actions, it cannot be directly applied to social impact evaluation. In this paper, the authors introduce a new method inspired by FMEA. The new method uses the traditional FMEA structure with essential modifications/extensions that allow any product to be analyzed relative to any of the 11 social impact categories. To avoid confusion with traditional FMEA, the new method is referred to as Social Impacts Effects Analysis (SIEA). In order to aid readability and provide a basis for understanding how SIEA works, the paper is organized by first presenting the limitations of FMEA as it applies to social impact evaluation (Section 2), then a step-by-step process for performing an SIEA is presented in Section 3; it is in this section that new developments are introduced. This is followed by an example SIEA in Section 4. Section 5 discusses the new developments in further detail after the reader is introduced to the method.

2. Limitations of FMEA for social impact evaluation

There are five areas identified by the authors where new developments are needed in order to make FMEA useful for evaluating the full range of social impact categories identified by Rainock et al. (Rainock et al., Reference Rainock, Everett, Pack, Dahlin and Mattson2018). They are:

  • Range of Impact Consideration- FMEA, by design, typically analyzes Health & Safety related risks. Health and Safety, however, is only 1 of the 11 Social Impact Categories (Rainock et al., Reference Rainock, Everett, Pack, Dahlin and Mattson2018). Furthermore, products with social impacts typically have impacts in many categories (Ottosson et al., Reference Ottosson, Mattson and Dahlin2020). While FMEA in its current form can be used for analyzing risk in other social impact categories, these instances have been rare exceptions and were limited in their consideration. Literature reviewed for this found FMEAs that analyzed social impacts in 8 of 11 categories (see Section 5.1), considering between 1 and 2 impact categories at a time. FMEA’s focus on Health and Safety, as well as the limited range of consideration, is insufficient to fully understand a product’s complete social impact and would limit a design team’s evaluation.

  • Duality of Product Effects- Products can have both positive and negative impacts with large effects on stakeholders (Benoît et al., Reference Benoît, Norris, Valdivia, Ciroth, Moberg, Bos, Prakash, Ugaya and Beck2010; Fontes et al., Reference Fontes, Tarne, Traverso and Bernstein2018). These impacts can be intentional or unintentional and should be considered in the design of a product (Stevenson et al., Reference Stevenson, Mattson, Bryden and MacCarty2018; Stringham et al., Reference Stringham, Smith, Mattson and Dahlin2020). However, FMEA typically deals with the occurrence of negative events and not with the positive impacts of products (Ginn et al., Reference Ginn, Jones, Rahnejat and Zairi1998). While this is valuable for FMEA’s designated purpose of considering failure modes, it does not help a designer consider the full positive and negative social impacts of their products. Not only does understanding the positive impacts help a designer better understand their product, it also allows a designer to consider how the positive and negative impacts are related, as well as the trade-offs between all impacts.

  • Consideration of Stakeholders- Social impacts are highly dependent on context and the differences between users, communities, and environments (Vanclay, Reference Vanclay2002; Fontes, Reference Fontes2016; Epstein and Yuthas, Reference Epstein and Yuthas2014). Social impacts also depend on both the product and the user, which requires different considerations for differing stakeholders (Stevenson et al., Reference Stevenson, Mattson, Bryden and MacCarty2018). FMEA generally considers a single stakeholder group, with the severity of failure effects being the same for most users in the stakeholder group. In cases where differences in magnitude occur, FMEA typically considers only the worst-case scenario (Stamatis, Reference Stamatis2003). Considering only a single stakeholder group limits a designer from fully understanding the social impact of their product across different segments of society.

  • Pattern of Occurrences- The social impact of products can occur both discretely (a single occurrence) and continuously (across extended periods of time). In fact, social sustainability is based on the notion that products can impact individuals and communities over an extended period of time (Graham Trotman/Martinus Nijhoff, Reference London1993; Desa and Koch, Reference Desa and Koch2014). FMEA is designed to deal with the risks of failure events, which are single discrete occurrences (Rose, Reference Rose2013). These discrete events have varying frequencies and can occur individually or concurrently (Sharma and Srivastava, Reference Sharma and Srivastava2018). While this works well for FMEA’s current usage analyzing failure modes, it would limit a designer from seeing all impacts their product may have. Examining both discrete and continuous occurrences creates a more complete view of a product’s immediate and sustained impact on users.

  • Uncertainty of Impact- FMEA typically only handles uncertainty related to detecting randomly occurring events, as shown in every failure mode being given a detectability score. However, the social impact of products contains many sources of uncertainty, such as uncertainty related to product adoption and use (Cohen et al., Reference Cohen, Lobel and Perakis2016), level of impact (Stevenson et al., Reference Stevenson, Mattson, Bryden and MacCarty2018), verification of impact occurrence, and uncertainty related to secondary effects or impacts (Jacobsen, Reference Jacobsen2015; Freeman, Reference Freeman2007). Broadening this area of consideration allows for a better understanding of how all the uncertainty related to a product could lead to an impact on people’s lives.

In contrast to traditional FMEA, SIEA encourages the consideration of a wide range of social impact categories, allows for both the negative and positive impacts of products, allows impact magnitude to be different for different user types, allows for impacts that are ongoing and not just one-time events, and considers additional types of uncertainty.

It is important to remember that, like any social impact assessment or design methodology, the success of the proposed SIEA is linked to the people performing the activity. Exploring the social impact of a product works better when those who know the problem deeply, both technically and socially, are involved (Wood et al., Reference Wood, Wood and Mattson2014). More diverse teams, such as multidisciplinary teams (Van Der Vegt and Bunderson, Reference Van Der Vegt and Bunderson2005), and teams that have diversity of gender, race, and ethnicity perform better (Ancona and Caldwell, Reference Ancona and Caldwell1992; Bear and Woolley, Reference Bear and Woolley2011). Working with those directly impacted and using a diverse team are recommended as part of performing SIEA.

3. Performing a social impacts effect analysis (SIEA)

In this section, the step-by-step process for performing a Social Impacts Effects Analysis is given. For clarity, a sample SIEA table is shown in Figure 1.

Figure 1. Sample SIEA table.

When choosing whether or not to perform an SIEA, designers should begin by assessing how known or unknown the product’s social impacts are to them. Products with strong expected impacts, newly developed products, and products being deployed in new areas or for new stakeholders are strong candidates for performing an SIEA (Lehmann et al., Reference Lehmann, Zschieschang, Traverso, Finkbeiner and Schebek2013; Akgün et al., Reference Akgün, Byrne, Lynn and Keskin2007).

The design team should also define stakeholder priorities before beginning the 15 steps below. Understanding stakeholder priorities is crucial to project success and is often best determined through direct communication with stakeholders using a variety of methods (Witmer, Reference Witmer2020). Determining stakeholder priorities at this step also makes assigning impact magnitudes easier and more accurate. Social impacts may have different magnitudes or occurrences for different stakeholder groups. If there are multiple groups of stakeholders with differing priorities, priorities should be defined for each group so impact ratings can be assigned separately for each.

As introduced in this paper, the 15 Steps for completing a SIEA are:

  1. 1. Determine Stakeholder Groups: List all stakeholders groups for the product being analyzed. These stakeholders include those who will use the product or be affected by its use. These stakeholders will be attached to each product attribute later in order to identify a product’s impact on each specific stakeholder group. See Column C1 in Figure 1.

  2. 2. List Product Attributes: List all attributes of the product at the relevant detail level. An attribute is defined here as a characteristic that describes part of the product’s form or function. For the early stages of design (before the product is defined), designers may list product requirements or expected features. In later stages, the design can be broken down into subsystems, features, or components. The goal of this step is to list many of the possible attributes so that effects and impacts may be assigned to them. See Column C2 in Figure 1.

  3. 3. List the Social Impacts of Product Attributes: List the impacts the product has on the stakeholders. See Column C3 in Figure 1. If different impacts exist for different stakeholders, assign each impact to its respective stakeholder group. Notice how Column C3 matches Column C1 with a different impact for each stakeholder group.

  4. 4. Categorize Social Impacts: Social impacts can be assigned to one or more of 11 major Social Impact Categories: Population Change, Family, Gender, Education, Paid Work, Stratification, Health and Safety, Human Rights, Social Networks and Communication, Conflict and Crime, and Cultural Heritage and Identity (Rainock et al., Reference Rainock, Everett, Pack, Dahlin and Mattson2018). See Column C4 in Figure 1.

  5. 5. List the Cause of Each Social Impact: Describe how the product attribute leads to the social impact on stakeholders. Describing this connection will help designers later determine how to adjust the design of the product to improve the social impacts of the product. See Column C5 in Figure 1.

  6. 6. Indicate Each Impact as Positive or Negative: Define each social impact as having a positive or negative effect on the stakeholder. See Column C6 in Figure 1. It is possible that a particular impact could be both positive and negative. If this is the case, the impact should be listed twice, once as a positive impact and once as a negative impact.

  7. 7. Indicate Each Impact as Continuous or Discrete: Define each social impact as occurring discretely or continuously. This refers to whether a specific impact will affect the user a single time or on an ongoing basis. See Column C7 in Figure 1.

  8. 8. Rank the Magnitude of Each Impact: Rate the magnitude of each social impact on a scale of 1–10. This is a measurement of how much the impact affects the life of the stakeholder. Table 1 gives an example scale for rating magnitudes. See Column C8 in Figure 1.

    Table 1. Impact magnitude rating table

  9. 9. Rank the Occurrence Likelihood of Each Impact: Rate the likelihood of occurrence of each social impact on a scale of 1–10. This is a measurement of the likelihood of a given impact happening. Different ways of considering impact occurrence are given in Section 5.4. Table 2 gives an example scale for rating occurrence. See Column C9 in Figure 1.

    Table 2. Impact occurrence rating table

  10. 10. Rank the Uncertainty of Each Impact: Rate the uncertainty of each social impact on a scale of 1–10. Uncertainty is a measure of how much uncertainty there is about the occurrence or magnitude of a given impact. Additional information is given in Section 5.5. Table 3 gives an example scale for rating uncertainty. See Column C10 in Figure 1.

    Table 3. Impact uncertainty rating table

  11. 11. Calculate Impact Priority Numbers:

    The Social Impact Risk Priority Number (IPN) is calculated differently depending on the sign of the impact. For negative impacts, the IPN is calculated by multiplying the Uncertainty minus 11, Magnitude, and Occurrence ratings. The scores range from −1 to −1000, with −1000 being the harmful impact most deserving of design resources. For positive impacts, multiply together 11 minus the Uncertainty, the Magnitude, and the Occurrence ratings. The scores range from 1 to 1000, with 1000 being the most beneficial impact. See Equation 1 and Column C11 in Figure 1.

    Additional Impact Priority Number calculations have been developed by the authors to help designers identify other positive impacts of interest, such as items with high potential for impact but either a low magnitude (Magnitude Priority Number, or MPN), low occurrence (Occurrence Priority Number, or OPN), or high uncertainty (Uncertainty Priority Number, or UPN). These calculations can be ranked with the highest numbers being those with the greatest opportunity to improve the $ IPN $ by improving that category. See Equations 2, 3, and 4. Note that for clarity, the scores for Magnitude, Occurrence and Uncertainty are represented (respectively) as $ M $ , $ O $ , and $ U $ in the equations.

  12. 12. Order Positive and Negative Impacts: Ranking impacts allow designers to see which impacts have the highest positive and negative values and therefore see which impacts need action. These actions are meant to change the impact of the design to acceptable levels. In this paper we call these impact management measures, which are discussed in greater detail in Section 5.2. Generally, it is recommended that designers consider all impacts with an $ IPN $ below −343 for product development resources and any impact with an uncertainty score 7 or higher for research resources so that uncertainty can be minimized in the future.

    For negative impacts, large negative numbers indicate which impacts would potentially be the most harmful. The largest negative impacts are those with high magnitude, high occurrence, and low uncertainty. These impacts are most deserving of immediate design resources because the designers are certain that this product attribute will have a large and frequent negative impact. Once the largest potential negative impacts are identified, action can be taken to mitigate those negative impacts.

    For positive impacts, large positive numbers indicate which impacts could be the most beneficial. These impacts have high magnitude, high occurrence, and low uncertainty. These are the most beneficial impacts because the designers can be sure that this attribute will have a large and frequent positive impact. When acting on positive $ IPN $ values, there are several approaches to take. One approach is to assign impact management measures to the impacts with the largest positive $ IPN $ to ensure that these impacts stay high. Another approach is to assign impact management measures to impacts with low positives $ IPN $ in order to improve these impacts. Both approaches have merit and may be used by the design team.

  13. 13. Assign Impact Management Measures: Impact Management Measures are specific actions assigned to team members to improve positive impacts or decrease negative impacts. These assigned activities are designed to change either the magnitude, occurrence, or uncertainty of the impact. See Column C12 in Figure 1.

  14. 14. Re-score Magnitude, Occurrence, and Uncertainty for Impacts with Management Measures: Adjust Magnitude, Occurrence, and Uncertainty scores as necessary to reflect expected changes as the result of Impact Management Measures. See Columns C13-C16 in Figure 1.

  15. 15. Follow Up: Perform follow-up to ensure that Impact Management Measures have the intended effect.

(1) $$ IPN=\left\{\begin{array}{ll}M\ast O\ast \left(U-11\right),& Negative\ Impact\\ {}M\ast O\ast \left(11-U\right),& Positive\ Impact\end{array}\right. $$
(2) $$ MPN=\left({O}^2-{M}^2\right)\ast \left(11-U\right) $$
(3) $$ OPN=\left({M}^2-{O}^2\right)\ast \left(11-U\right) $$
(4) $$ UPN=\left(U-1\right)\ast \left(M\ast O\right) $$

4. Illustration/example

Figure 1 shows several rows of an example SIEA performed by the authors. The exercise examined the social impacts of a modular solar charger produced by Fenix and designed for use in rural Uganda. Due to size constraints, only eight rows of the example SIEA are listed in this paper.

Column C1 lists the stakeholders/users of the solar charger, which in this example are: households in Uganda, children in the households, women in the households, and employed members of the households. Column C2 lists product requirements or features such as mobile payment and mobile locking of the modular solar charger. Column C3 lists the social impacts of the product features, such as increased electricity access for work purposes, educational purposes, and women in the households. Column C4 lists which impact category each impact belongs to, such as Paid Labor or Education. Column C5 lists the impact causes, such as mobile payment availability and lower monthly payment costs, which make the device more accessible. Column C6 lists whether the designers considered each impact as positive or negative. For example, increased electricity access was classified as a positive impact, and the ability of the solar company to lock out users was classified as a negative impact for the user stakeholder group. Columns C6, C7, and C8 are the designer ratings for impact magnitude, likelihood, and uncertainty. Column C11 shows the calculated Impact Priority Number $ IPN $ for each impact. These $ IPN $ s were used by the designers to rank impacts by priority and assign actions to increase positive impacts and decrease negative impacts. Column C12 lists suggested impact management measures such as ensuring customer service assistance is available to help customers who are mistakenly locked out of their solar chargers. Columns C13, C14, and C15 list new rankings for impact magnitude, likelihood, and uncertainty after suggested actions are taken. Column C16 lists the new $ IPN $ scores and Column C17 lists the expected improvement due to the impact management measures.

For reference, completing this SIEA took 3 designers 3 hours to complete and analyzed 42 potential impacts related to 11 product attributes in 7 social impact categories (Education, Family, Gender, Health and Safety, Human Rights, Paid Labor, and Social Networks and Communication). While more time could be spent and more social impact categories could be analyzed, this illustration demonstrates how an SIEA could realistically be used to help designers consider a wide range of impacts from different social impact categories in a timely manner.

This exercise also helped designers see how each of four different stakeholder groups (Households in Uganda, Employed Members of Households, Women in Households, Children in Households) were affected differently by the product. The activity also connected the 42 potential impacts to 11 product attributes. These connections are an important feature of FMEAs that help designers understand how product performance leads to impact, as well as the trade-offs and relationships between product performance and impact for multiple stakeholder groups.

And finally, the calculation of Impact Priority Numbers allowed all 42 potential impacts to be ranked to help determine designer priorities for maximizing positive impact and minimizing negative impact. The four impact priority methods given in Section 3, step 11 (Traditional Impact Priority Number, Magnitude Priority Number, Occurrence Magnitude Number, and Uncertainty Magnitude Number) were used to calculate the highest overall positive and negative impacts as well as high potential targets for improving the magnitude, occurrence, and uncertainty.

Of the impacts shown in Figure 1, the largest positive impacts identified were the impact of increased electricity access due to the cost of the charger. The largest negative impact was electrical shock due to the charger being damaged. The greatest opportunity to increase impact through occurrence was ensuring that the device functions reliably in portable work conditions. The largest opportunity for increasing impact through magnitude was the impact on education by allowing the continual charging of devices in educational settings. The largest opportunity to increase impact by decreasing uncertainty was the impact of increased electricity access for all family members. Identifying the most impactful changes is an important part of project evaluation and creating plans to maximize positive impacts and minimize negative impacts (Watts et al., Reference Watts, Smith and Thomson2016).

These rankings illustrate how the FMEA approach helps designers not only create a large list of potential impacts but also rank and prioritize which impacts need additional consideration in the design process. Focusing on the highest priority impacts identified increased the overall impacts by both decreasing negative impacts and increasing positive impacts of the product.

5. Highlighting differences between SIEA and FMEA

This section describes the attributes of SIEA in greater detail and how it compares to traditional FMEA. As previously stated, FMEA could not be directly applied to social impact evaluation for five main reasons. Now that SIEA has been introduced and explained, these main reasons can be explained in greater depth. Note that these five changes, as well as additional differences, are summarized in Table 4.

Table 4. FMEA and SIEA comparison

5.1. Social impact consideration range

SIEA aims to help designers consider more relevant social impacts in a wider range of impact categories than methods currently practiced. This method encourages designers to consider more social impacts by systematically listing social impacts for every aspect of the product. Products typically have impacts in multiple social impact categories (Ottosson et al., Reference Ottosson, Mattson and Dahlin2020), which is why SIEA guides designers in considering a broad range of impacts across categories.

As acknowledged in the beginning of the paper, on few occasions FMEA has been used to analyze effects in 8 of the 11 impact categories put forth by Rainock et al (Rainock et al., Reference Rainock, Everett, Pack, Dahlin and Mattson2018). The impact categories analyzed include: Conflict & Crime (Rao et al., Reference Rao, Tharmavaram and Pandey2020) (Stefankova et al., Reference Stefankova, Balog and Raksany2014), Education (Sutrisno and Lee, Reference Sutrisno and Lee2011), Family (Neisiani et al., Reference Neisiani, Seyedan and Hadian2016), Gender (Ranangen et al., Reference Ranängen, Cöster, Isaksson and Garvare2018), Health & Safety (Zeng et al., Reference Zeng, Tam and Tam2010) (Latino and Flood, Reference Latino and Flood2004) (Chiozza and Ponzetti, Reference Chiozza and Ponzetti2009), Human Rights (H˛abek and Molenda, Reference Hąbek and Molenda2017), Paid Work (Bahrami et al., Reference Bahrami, Bazzaz and Sajjadi2012) (Santos and Cabral, Reference Santos and Cabral2008) (Carbone and Tippett, Reference Carbone and Tippett2004), and Social Networks & Communication (Chandra et al., Reference Chandra, Ratna and Ramli2020). FMEA has also been used to analyze environmental impact (Zeng et al., Reference Zeng, Tam and Tam2010; Vazdani et al., Reference Vazdani, Sabzghabaei, Dashti, Cheraghi, Alizadeh and Hemmati2017; Roszak et al., Reference Roszak, Spilka and Kania2015). While these studies have occurred, they have been rare exceptions and are only done 1–2 categories at a time. SIEA differs from FMEA in this case because it is designed for situations such as these and is built to provide simultaneous consideration of a wide range of impacts. The example in Section 4 illustrates the broad range of social impacts for an SIEA performed on a modular solar charger, finding impacts related to 7 different social impact categories.

5.2. Product effect duality

SIEA assigns each impact as being either positive or negative. Considering impacts as positive or negative helps designers know which positive impacts need to be protected and which negative impacts need to be mitigated or prevented (Stevenson et al., Reference Stevenson, Mattson, Bryden and MacCarty2018). Whether an impact is considered positive or negative can vary for stakeholders, as a product may produce positive impacts for one user and negative impacts for another (Rainock et al., Reference Rainock, Everett, Pack, Dahlin and Mattson2018). Industrial equipment, for example, may increase profits for its owner but could pose a safety risk to users and create pollution and noise that negatively impacts the community. Often these impacts are paired and lead to trade-offs (Pugel and Walters, Reference Pugel and Walters2017).

Additionally, products often have secondary effects where the benefit of a product leads to a change in behavior, which creates additional impacts (Bhamra et al., Reference Bhamra, Lilley and Tang2011). For example, farming equipment that improves farm output could improve wages for employees of farmers that own the equipment, or the increase in efficiency could lead to fewer employees or other laborers. Increased production could negatively impact competing farmers. Positive social impacts may produce negative secondary impacts, and negative social impacts may produce positive secondary impacts. Secondary effects are important to consider because they are often overlooked. Unconsidered secondary impacts have been observed as a source of project failure in global development projects (Jacobsen, Reference Jacobsen2015; Freeman, Reference Freeman2007).

Considering both positive and negative impacts simultaneously offers an improvement to several current risk management methodologies, such as FMEA, that only consider negative impacts (Ginn et al., Reference Ginn, Jones, Rahnejat and Zairi1998). The assignment of positive or negative also goes toward calculating the Impact Priority Number, which is used for ranking and prioritizing product impacts. There are differences in how positive and negative impact scores are ranked and the strategies designers use to increase positive impact and decrease negative impacts.

The ultimate goal of SIEA is to consider many of the possible impacts and rank them so that resources can be dedicated to the most important impacts (Xiao et al., Reference Xiao, Huang, Li, He and Jin2011; Chen, Reference Chen2007). After impacts have been ranked by their $ IPN $ , the design team assigns specific actions to improve the impacts and delegates these actions to team members. These corrective actions aim to reduce negative impacts and increase positive impacts by changing the magnitude, occurrence, or uncertainty of selected impacts (Van Leeuwen et al., Reference Van Leeuwen, Nauta, De Kaste, Odekerken-Rombouts, Oldenhof, Vredenbregt and Barends2009).

Multiple possible corrective actions can be taken that may have different effectiveness and costs. The design team decides which corrective actions would be the most appropriate and assigns the action to a specific member of the design team (Paciarotti et al., Reference Paciarotti, Mazzuto and D’Ettorre2014). The right corrective actions in the early stages of design can prevent more costly corrective actions later (Paciarotti et al., Reference Paciarotti, Mazzuto and D’Ettorre2014). There are several ways to determine how many impacts should be assigned management measures. These ways include using an $ IPN $ threshold, assigning actions to a percentage of impacts with the highest $ IPN $ s, using a screening matrix, or using a graph of $ IPN $ s to find the inflection point for impact priorities (Mikulak et al., Reference Mikulak, McDermott and Beauregard2017; Sankar and Prabhu, Reference Sankar and Prabhu2001; Catelani et al., Reference Catelani, Ciani, Galar and Patrizi2020).

5.3. Stakeholder consideration

Social impacts depend on both the product and the user (Stevenson et al., Reference Stevenson, Mattson, Bryden and MacCarty2018). Individuals have many differences including differences, in physical attributes, access to resources, cultural upbringing, needs, desires, and priorities. Because social impacts are closely related to stakeholder values, SIEA starts by attempting to identify and understand the priorities of the major relevant stakeholders. This can be done through a variety of methods, such as using personas or including stakeholders in participatory or co-design (Ogawa and Piller, Reference Ogawa and Piller2006; Wilkinson and De Angeli, Reference Wilkinson and De Angeli2014; Schuler and Namioka, Reference Schuler and Namioka1993).

The other main difference is that SIEA handles stakeholder differences by evaluating impact magnitudes separately for each major stakeholder group. This helps design teams consider the most important impacts for each stakeholder group and understand trade-offs between stakeholders. This information helps design teams handle trade-offs better and create a product with desirable impacts (Wong, Reference Wong2005).

5.4. Occurrence pattern

Several methods used in engineering handle either impacts related to discrete events or the continuous impacts of products (Rose, Reference Rose2013). For example, FMEA is used to analyze discrete events but not continuous impacts. In contrast, SIEA has been designed to deal with both the discrete and continuous impacts of products. This is important because events that cause impacts can either be discrete, such as a one-time medication that relieves symptoms for a few hours, or continuous, such as the clean water a well supplies to a village 24 hours a day. Additionally, discrete events can create continuous, lasting impacts, such as an injury caused by a product having lasting health effects. Events that continuously provide an impact while in use might also provide little benefit after use of the product has ended, such as an emergency shelter. Some products might not be used continuously, but the availability of use provides an impact, such as a cell phone that provides benefits only while in use, but the ability to use the phone at any time creates a continuous positive impact.

Whether an impact can be thought of as continuous or discrete, all impact causes and impact effects can be described as having an occurrence likelihood. Mathematically, this is a probability or percentage between 0–1 or 0%–00%. Defining occurrence in this way is robust mathematically but is potentially problematic in the context of occurrence ratings that occur in FMEA and other methods. The two main issues with this are that impacts can occur across a broad spectrum of occurrences and that the value judgements associated with assigning an occurrence number vary depending on the individual impacts.

For example, a knee brace could provide stability and improved healing for 19 out of 20 patients, cause irritation in 5 out of 20 patients, and lead to a serious accident by snagging on heavy equipment or moving objects 1 time per 200,000 hours of patient use. Linear and potentially even logarithmic scales may have difficulty providing the right level of resolution across the potential impacts of a product. Furthermore, what qualifies as a low or high occurrence depends on the individual impact. In the previous example, 1 serious injury per 200,000 hours of patient use might be considered a high-occurrence event in need of mitigation, while the 5 in 20 occurrence of irritation might be considered a low-occurrence event that does not need additional design consideration. Some of these issues are resolved by the overall impact score, which accounts for the magnitude and uncertainty of impacts; however, some issues may remain.

There are several approaches to handling these irregularities. The authors present four options that have different strengths and drawbacks that provide flexibility for the best use in different applications or situations.

  1. 1. Use a linear occurrence scale related to the mathematical probability of occurrence and a range that encompasses the impacts identified. This approach is straightforward and intuitive mathematically. Potential scaling issues may be resolved with additional impact ranking metrics discussed in Section 3, step 11.

  2. 2. Use the mathematical probability of occurrence on a logarithmic scale. This approach handles large ranges of occurrence well and provides good resolution across such large differences. However, this approach is slightly less intuitive and may involve additional calculations.

  3. 3. Consider the occurrence in a qualitative manner instead of a strictly mathematical assignment. As discussed previously, whether an impact is considered a low occurrence or high occurrence depends on the impact itself. This approach allows designers the flexibility to make these value judgements. This approach might not be as mathematically rigorous or repeatable, but it may be a more appropriate approach when the effects of product impacts span a very large range. This approach is demonstrated in Table 2 in Section 3.

  4. 4. Rank occurrence based on the likelihood that the design team can design the product to achieve the desired level of impact. This approach is applicable early in the product design before mathematical probabilities can be known and helps the design team focus on the areas of design that need the most attention to achieve the desired impact.

5.5. Impact uncertainty

An important aspect of social impact consideration is uncertainty (Leung et al., Reference Leung, Noble, Gunn and Jaeger2015). There are several types of uncertainty associated with social impacts. For designers, there is uncertainty about the actual impact a product has on the lives of users (Stevenson et al., Reference Stevenson, Mattson, Bryden and MacCarty2018). There is also uncertainty about the adoption or acceptance of the product (Cohen et al., Reference Cohen, Lobel and Perakis2016). Additional uncertainty comes from the potential for secondary impacts or effects (Jacobsen, Reference Jacobsen2015; Freeman, Reference Freeman2007).

There are several sources for the uncertainty of impacts on the user side as well. There is uncertainty associated with the occurrence of random events. In traditional FMEA, this is referred to as detectability. Increasing the detectability decreases uncertainty by allowing users to foresee a potential failure before the failure and its negative effects occur. There is also uncertainty for the user about whether the use of a product creates an impact. For example, the health benefits of clean water or an improved cookstove may not be immediately apparent to users. This type of uncertainty can affect the probability that an individual will use a product (Au and Enderwick, Reference Au and Enderwick2000). This type of uncertainty is also challenging for those who wish to measure or quantify the impact of products.

As designers, it is desirable to reduce all of these uncertainties. Areas of high uncertainty signal the need to use research resources to reduce uncertainty. When it comes to ranking uncertainty for use in an SIEA, there are several possible approaches with varying strengths and weaknesses. These approaches are as follows:

  1. 1. Focus on only one type of uncertainty. This approach only considers one source of uncertainty at a time. This is a simple approach that also tailors to the different stages of design. In conceptual stages, designers may rate the uncertainty associated with designing the product, and later stages may then progressively focus on the uncertainty associated with levels of impact, product acceptance, and verifiability of the impact occurring.

  2. 2. Consider multiple sources of uncertainty. This approach ranks each type of uncertainty separately. This approach is beneficial in that it considers many types of uncertainty; however, it increases the time required to perform an SIEA and could complicate $ IPN $ rating calculations and ordering.

  3. 3. Consider only the largest uncertainty. While several sources of uncertainty exist for all impacts, some may be of greater concern for individual product impacts. Ranking the largest source of uncertainty for each impact lowers the amount of rankings and calculations needed, but it adds complexity as it requires designers to compare different sources of uncertainty mentally.

  4. 4. Use a holistic approach. This approach relies on the intuition and experience of users to consider the overall uncertainty from all sources. This approach is not as well defined, but it has the potential to cover the breadth of uncertainty types without requiring the time put into a deep analysis of each type individually.

6. Discussion and concluding remarks

SIEA is built on the aspects of FMEA that are attractive for analyzing the social impact of engineered products, such as the structured methodical approach and qualitative rankings that allow for the comparison of impacts. SIEA differs from the traditional FMEA approach to allow for full consideration of social impacts by a design team. These necessary changes include handling impact differences for multiple stakeholders, evaluating social impacts from a broader range of categories, allowing for continuous and discrete impacts, assigning impacts as either positive or negative, and considering a wide range of the uncertainty associated with the social impact.

In addition to SIEA having the benefit of the methodical and qualitative FMEA approach, using a method similar to current practices may help avoid unnecessary complexity and help increase implementation and adoption (Tajima and Fischer, Reference Tajima and Fischer2013). SIEA is also an attractive method because the qualitative approach borrowed from FMEA is less costly and thus more likely to be implemented than other social impact assessment methods that require large amounts of data (Henry, Reference Henry1990).

Future work could include controlled experiments or case studies to determine the performance of SIEA in improving social impact considerations in the product development process. While SIEA cannot follow the same adoption pattern as FMEA (which was created and applied purely in an industry setting), controlled experiments or case studies could provide valuable information on the value of SIEA before industry can rely on this method like they rely on traditional FMEA.

In conclusion, the authors believe that the same methodical approach that has made FMEA successful in many fields (such as product development, risk management, and quality management) could be applied for use as a dedicated social impact analysis method. This method, Social Impact Effects Analysis (SIEA), builds upon FMEA to allow designers to more fully consider the social impacts of their product. Made by combining the desirable features of FMEA with the necessary changes for a focus on social impact evaluation, SIEA provides a method to make social impact analysis more accessible and effective to aid in the development of products with improved social impact.

Financial support

The authors gratefully acknowledge the support of the National Science Foundation grant CMMI-17651505 that funded this research. Any opinions, findings, conclusions, or recommendations expressed in this material are those of the authors and do not necessarily reflect the views of the National Science Foundation.

References

Akgün, A. E., Byrne, J. C., Lynn, G. S. & Keskin, H. 2007. New product development in turbulent environments: Impact of improvisation and unlearning on new product performance. Journal of Engineering and Technology Management 24(3), 203230.CrossRefGoogle Scholar
Ancona, D. G. & Caldwell, D. F. 1992. Demography and design: Predictors of new product team performance. Organization Science 3(3), 321341.CrossRefGoogle Scholar
Asiedu, Y. & Gu, P. 1998 Product life cycle cost analysis: state of the art review. International Journal of Production Research 36(4), 883908.CrossRefGoogle Scholar
Au, A. K.-m. & Enderwick, P. 2000 A cognitive model on attitude towards technology adoption. Journal of Managerial Psychology 15(4), 266282.Google Scholar
Bahrami, M., Bazzaz, D. H. & Sajjadi, S. M. 2012 Innovation and improvements in project implementation and management; using fmea technique. Procedia-Social and Behavioral Sciences 41, 418425.CrossRefGoogle Scholar
Bear, J. B. & Woolley, A. W. 2011 The role of gender in team collaboration and performance. Interdisciplinary Science Reviews 36(2), 146153.CrossRefGoogle Scholar
Benoît, C., Norris, G. A., Valdivia, S., Ciroth, A., Moberg, A., Bos, U., Prakash, S., Ugaya, C. & Beck, T. 2010 The guidelines for social life cycle assessment of products: just in time! The International Journal of Life Cycle Assessment 15(2), 156163.CrossRefGoogle Scholar
Bhamra, T., Lilley, D. & Tang, T. 2011 Design for sustainable behaviour: Using products to change consumer behaviour. The Design Journal 14(4), 427445.CrossRefGoogle Scholar
Bonilla-Alicea, R. J. & Fu, K. 2019 Systematic map of the social impact assessment field. Sustainability 11(15), 4106.CrossRefGoogle Scholar
Breiing, A. & Kunz, A. 2002 Critical consideration and improvement of the fmea. In Proceedings of Tools and Methods of Competitive Engineering-TMCE 2002, 2002, pp. 519530 Wuhan, China.Google Scholar
Burdge, R. J. 1995 A community Guide to Social Impact Assessment. Dog Eared Pub.Google Scholar
Burleson, G., Sienko, K. H. & Toyama, K. 2020 Incorporating contextual factors into a design process: An analysis of engineering for global development literature. In International Design Engineering Technical Conferences and Computers and Information in Engineering Conference, volume 84010, pp. V11BT11A009. American Society of Mechanical Engineers.CrossRefGoogle Scholar
Carbone, T. A. & Tippett, D. D. 2004 Project risk management using the project risk fmea. Engineering Management Journal 16(4), 2835.CrossRefGoogle Scholar
Carlson, C. S. 2014 Understanding and applying the fundamentals of fmeas. Annual Reliability and Maintainability Symposium 10, 135.Google Scholar
Catelani, M., Ciani, L., Galar, D. & Patrizi, G. 2020 Risk assessment of a wind turbine: A new fmeca-based tool with rpn threshold estimation. IEEE Access 8, 2018120190.CrossRefGoogle Scholar
Chandra, N. A., Ratna, A. A. P. & Ramli, K. 2020 Development of a cyber-situational awareness model of risk maturity using fuzzy fmea. In International Workshop on Big Data and Information Security (IWBIS), pp. 127136. IEEE.Google Scholar
Chen, J. K. 2007 Utility priority number evaluation for fmea. Journal of Failure Analysis and Prevention 7(5), 321328.CrossRefGoogle Scholar
Chiozza, M. L. & Ponzetti, C. 2009 Fmea: A model for reducing medical errors. Clinica Chimica Acta 404(1), 7578.CrossRefGoogle Scholar
Cohen, M. C., Lobel, R. & Perakis, G. 2016 The impact of demand uncertainty on consumer subsidies for green technology adoption. Management Science 62(5), 12351258.CrossRefGoogle Scholar
de Aguiar, D. C., Salomon, V. A. P. & Mello, C. H. P. 2015 An iso 9001 based approach for the implementation of process fmea in the brazilian automotive industry. International Journal of Quality & Reliability Management.CrossRefGoogle Scholar
Desa, G. & Koch, J. L. 2014 Scaling social impact: Building sustainable social ventures at the base-of-the-pyramid. Journal of Social Entrepreneurship 5(2), 146174.CrossRefGoogle Scholar
Dudek-Burlikowska, M. 2011 Application of fmea method in enterprise focused on quality. Journal of Achievements in Materials and Manufacturing Engineering 45(1), 89102.Google Scholar
Epstein, M. J. & Yuthas, K. 2014 Measuring and Improving Social Impacts: A Guide for Nonprofits, Companies, and Impact Investors. Berrett-Koehler Publishers.Google Scholar
Esteves, A. M., Franks, D. & Vanclay, F. 2012 Social impact assessment: the state of the art. Impact Assessment and Project Appraisal, 30(1), 3442.CrossRefGoogle Scholar
Fontes, J. 2016 Handbook-for-product-social-impact. Assessment 3(3).Google Scholar
Fontes, J., Tarne, P., Traverso, M. & Bernstein, P. 2018. Product social impact assessment. The International Journal of Life Cycle Assessment 23(3), 547555.CrossRefGoogle Scholar
Freeman, J. M. 2007. Beware: The misuse of technology and the law of unintended consequences. Neurotherapeutics 4(3), 549554.CrossRefGoogle ScholarPubMed
Ginn, D., Jones, D., Rahnejat, H. & Zairi, M. 1998. The “qfd/fmea interface”. European Journal of Innovation Management 1(1), 720.Google Scholar
Graham and Trotman/Martinus Nijhoff, London, B. 1993 nited nations conference on environment and development. In The Earth Summit: the United Nations Conference on Environment and Development (UNCED), volume vi, pp. 532. United Nations Conference on Environment and Development.Google Scholar
Hąbek, P. & Molenda, M. 2017 Using the fmea method as a support for improving the social responsibility of a company. In International Conference on Operations Research and Enterprise Systems, volume 2, pp. 57–65. SCITEPRESS.CrossRefGoogle Scholar
Hallstedt, S., Isaksson, O., Nylander, J. W., Andersson, P. & Knuts, S. 2023 Sustainable product development in aeroengine manufacturing: challenges, opportunities and experiences from gkn aerospace engine system. Design Science 9, e22.CrossRefGoogle Scholar
Hendrickson, C., Horvath, A., Joshi, S. & Lave, L. 1998 Peer reviewed: economic input–output models for environmental life-cycle assessment. Environmental Science & Technology 32(7), 184A191A.CrossRefGoogle Scholar
Henry, R. 1990 Implementing social impact assessment in developing countries: A comparative approach to the structural problems. Environmental Impact Assessment Review 10(1–2), 91101.CrossRefGoogle Scholar
Jacobsen, K. L. 2015 The Politics of Humanitarian Technology: Good Intentions, Unintended Consequences and Insecurity. Routledge.CrossRefGoogle Scholar
Jørgensen, A., Le Bocq, A., Nazarkina, L. & Hauschild, M. 2008 Methodologies for social life cycle assessment. The International Journal of Life Cycle Assessment 13(2), 96103.CrossRefGoogle Scholar
Joshi, S. 1999. Product environmental life-cycle assessment using input-output techniques. Journal of Industrial Ecology 3(2–3), 95120.CrossRefGoogle Scholar
Kirkire, M. S., Rane, S. B. & Jadhav, J. R. 2015. Risk management in medical product development process using traditional fmea and fuzzy linguistic approach: A case study. Journal of Industrial Engineering International 11(4), 595611.CrossRefGoogle Scholar
Latino, R. J. & Flood, A. 2004 Optimizing fmea and rca efforts in health care. Journal of Healthcare Risk Management 24(3), 2128.CrossRefGoogle ScholarPubMed
Lehmann, A., Zschieschang, E., Traverso, M., Finkbeiner, M. & Schebek, L. 2013 Social aspects for sustainability assessment of technologies—challenges for social life cycle assessment (slca). The International Journal of Life Cycle Assessment 18(8), 15811592.CrossRefGoogle Scholar
Leung, W., Noble, B., Gunn, J. & Jaeger, J. A. 2015 A review of uncertainty research in impact assessment. Environmental Impact Assessment Review 50, 116123.CrossRefGoogle Scholar
Mattson, C. A. and Sorensen, C. D. 2019 Product Development: Principles and Tools for Creating Desirable and Transferable Designs. Springer Nature.Google Scholar
Mikulak, R. J., McDermott, R. & Beauregard, M. 2017 The Basics of FMEA. CRC Press.Google Scholar
Neisiani, B. A., Seyedan, S. & Hadian, A. 2016 Implementation of child safety and health management system by means of fmea method. International Journal of Human Capital in Urban Management 1(1), 6572.Google Scholar
Ogawa, S. & Piller, F. T. 2006 Reducing the risks of new product development. MIT Sloan Management Review 47(2), 65.Google Scholar
Ottosson, H. J., Mattson, C. A & Dahlin, E. C. 2020 Analysis of perceived social impacts of existing products designed for the developing world, with implications for new product development. Journal of Mechanical Design 142(5).CrossRefGoogle Scholar
Paciarotti, C., Mazzuto, G. & D’Ettorre, D. 2014 A revised fmea application to the quality control management. International Journal of Quality & Reliability Management 31(7), 788810.Google Scholar
Pack, A. T., Rose Phipps, E., Mattson, C. A. & Dahlin, E. C. 2020 Social impact in product design, an exploration of current industry practices. Journal of Mechanical Design 142(7).CrossRefGoogle Scholar
Phillips, H., Renda, G. & McDonald, R. 2024 Design and assistive technology: A tinder match waiting to happen. Design Science 10, e5.CrossRefGoogle Scholar
Pugel, K. & Walters, J. P. 2017 Embedding systems thinking into ewb project planning and development: Assessing the utility of a group model building approach. Journal of Humanitarian Engineering 5(2).CrossRefGoogle Scholar
Rainock, M., Everett, D., Pack, A., Dahlin, E. C. & Mattson, C. A. 2018 The social impacts of products: a review. Impact Assessment and Project Appraisal 36(3), 230241.CrossRefGoogle Scholar
Ranängen, H., Cöster, M., Isaksson, R. & Garvare, R. 2018. From global goals and planetary boundaries to public governance—a framework for prioritizing organizational sustainability activities. Sustainability 10(8), 2741.CrossRefGoogle Scholar
Rao, P. K., Tharmavaram, M. & Pandey, G. 2020 Conventional technologies in forensic science. Technology in Forensic Science: Sampling, Analysis, Data and Regulations, pp. 17–34.Google Scholar
Richards, D. C., Stevenson, P. D., Mattson, C. A. & Salmon, J. L. 2023 An approach for including social impact measures in systems design exploration. Design Science 9, e16.CrossRefGoogle Scholar
Rose, K. H. 2013 A guide to the project management body of knowledge (pmbok® guide)—fifth edition. Project Management Journal 3(44), e1e1.CrossRefGoogle Scholar
Roszak, M., Spilka, M. & Kania, A. 2015. Environmental failure mode and effects analysis (fmea)–a new approach to methodology. Metalurgija 54(2), 449451.Google Scholar
Sankar, N. R. & Prabhu, B. S. 2001 Modified approach for prioritization of failures in a system failure mode and effects analysis. International Journal of Quality Reliability Management 18(3), 324336.CrossRefGoogle Scholar
Santos, F. R. S. d. & Cabral, S. 2008 Fmea and pmbok applied to project risk management. JISTEM-Journal of Information Systems and Technology Management 5(2), 347364.CrossRefGoogle Scholar
Schuler, D. & Namioka, A. 1993 Participatory Design: Principles and Practices. CRC Press.Google Scholar
Sharma, K. D. & Srivastava, S. 2018 Failure mode and effect analysis (fmea) implementation: a literature review. Journal of Advanced Research in Aeronautics and Space Science 5, 24548669.Google Scholar
Shebl, N. A., Franklin, B. D. & Barber, N. 2012 Failure mode and effects analysis outputs: Are they valid? BMC Health Services Research 12(1), 110.CrossRefGoogle ScholarPubMed
Stamatis, D. H. 2003 Failure Mode and Effect Analysis: FMEA from Theory to Execution. Quality Press.Google Scholar
Stefankova, J., Balog, K. & Raksany, P. 2014 Evaluation of the security situation abroad by the fmea method and impact of natural or technical threats on the environment. In Advanced Materials Research, volume 1001, pp. 469474. Trans Tech Publ.Google Scholar
Stevenson, P. D., Mattson, C. A., Bryden, K. M., and MacCarty, N. A. 2018 Toward a universal social impact metric for engineered products that alleviate poverty. Journal of Mechanical Design 140(4).CrossRefGoogle Scholar
Stringham, B. J., Smith, D. O., Mattson, C. A. & Dahlin, E. C. 2020 Combining direct and indirect user data for calculating social impact indicators of products in developing countries. Journal of Mechanical Design 142(12).CrossRefGoogle Scholar
Sutrisno, A. & Lee, T. 2011. Service reliability assessment using failure mode and effect analysis (fmea): survey and opportunity roadmap. International Journal of Engineering, Science and Technology 3(7), 2538.CrossRefGoogle Scholar
Tajima, R. & Fischer, T. B. 2013 Should different impact assessment instruments be integrated? evidence from english spatial planning. Environmental Impact Assessment Review 41, 2937.CrossRefGoogle Scholar
Udoewa, V. 2022). An introduction to radical participatory design: decolonising participatory design processes. Design Science 8, e31.CrossRefGoogle Scholar
Van Der Vegt, G. S. & Bunderson, J. S. 2005. Learning and performance in multidisciplinary teams: The importance of collective team identification. Academy of management Journal 48(3), 532547.CrossRefGoogle Scholar
Van Leeuwen, J., Nauta, M., De Kaste, D., Odekerken-Rombouts, Y., Oldenhof, M., Vredenbregt, M. & Barends, D. 2009 Risk analysis by fmea as an element of analytical validation. Journal of Pharmaceutical and Biomedical Analysis 50(5), 10851087.CrossRefGoogle Scholar
Vanclay, F. 2002 Conceptualising social impacts. Environmental Impact Assessment Review 22(3), 183211.CrossRefGoogle Scholar
Vazdani, S., Sabzghabaei, G., Dashti, S., Cheraghi, M., Alizadeh, R., Hemmati, A., et al. 2017 Fmea techniques used in environmental risk assessment. Environment & Ecosystem Science (EES) 1(2), 1618.CrossRefGoogle Scholar
Watts, R. A., Smith, J. Thomson, A. 2016 The design and installation of solar home systems in rural cambodia. Journal of Humanitarian Engineering 4(2).CrossRefGoogle Scholar
Wilkinson, C. R. & De Angeli, A. 2014 Applying user centred and participatory design approaches to commercial product development. Design Studies 35(6), 614631.CrossRefGoogle Scholar
Witmer, A.-P. 2020 Cultivating the assimilative perspective in contextual engineering–knowing what you don’t know. Journal of Humanitarian Engineering 8(1).CrossRefGoogle Scholar
Wong, B. 2005 Understanding stakeholder values as a means of dealing with stakeholder conflicts. Software Quality Journal 13(4), 429445.CrossRefGoogle Scholar
Wood, A. E., Wood, C. D. & Mattson, C. A. 2014. Application and modification of design for manufacture and assembly principles for the developing world. In IEEE Global Humanitarian Technology Conference (GHTC 2014), pp. 451457. IEEE.CrossRefGoogle Scholar
Wu, R., Yang, D. & Chen, J 2014 Social life cycle assessment revisited. Sustainability 6(7), 42004226.CrossRefGoogle Scholar
Xiao, N., Huang, H.-Z., Li, Y., He, L. & Jin, T. 2011. Multiple failure modes analysis and weighted risk priority number evaluation in fmea. Engineering Failure Analysis 18(4), 11621170.CrossRefGoogle Scholar
Zeng, S. X., Tam, C. M. & Tam, V. W. 2010 Integrating safety, environmental and quality risks for project management using a fmea method. Engineering Economics, 66(1).Google Scholar
Zhao, X. & Bai, X. 2010 The application of fmea method in the risk management of medical device during the lifecycle. In 2010 2nd International Conference on E-business and Information System Security, pp. 14. IEEE.CrossRefGoogle Scholar
Figure 0

Figure 1. Sample SIEA table.

Figure 1

Table 1. Impact magnitude rating table

Figure 2

Table 2. Impact occurrence rating table

Figure 3

Table 3. Impact uncertainty rating table

Figure 4

Table 4. FMEA and SIEA comparison