Wednesday, December 7, 2016

Voluntary Individual Pro-Environmental Behavior and Climate Change

by Robert T. Ernst, PhD

Note: this post is a version of an article published in the journal, Practicing Planner, in Fall 2013.

Introduction

It would be wonderful, in terms of decreased carbon footprint, if more people used fuel efficient cars and LED light bulbs, or rode bikes to work and to shop, or if more local political jurisdictions adopted climate change mitigation and adaptation  measures. It would be even better if most Americans lived in houses that produced more energy than they used, rejected energy- and carbon-intensive 21st Century lifestyles, and returned to residential and consumption patterns typical of 1950. But, other than making people feel better about prospects for their future, the question should be raised as to whether voluntary individual environmental virtue makes a difference in today’s world of climate change.

To be upfront, on this question I am a pessimist and do not believe what individuals or individual local political jurisdictions do voluntarily to cut carbon use makes a significant difference in terms of climate change. This statement is made despite my understanding that cities are engines of economic activity and as such generate the far greater majority of greenhouse gas emissions and are critical elements in climate change mitigation/adaptation strategies. The following materials help explain why I hold that conviction.

For sake of argument, let’s assume if every American and all local political jurisdictions practiced voluntary environmental virtue, on average that practice would reduce carbon dioxide use to quantities last recorded in 1950[1] when residential air conditioning was practically unknown, houses were much smaller, suburban sprawl was in its infancy, and cars, although larger and fuel inefficient, were significantly fewer in number and people traveled less. If everyone and all local political jurisdictions in the U.S. would change their lives and operations to conform to that assumption, personal production of CO2 would drop to about 8.5 tons annually and the country-wide total would fall to the general neighborhood of 2.65 billion tons.

Obviously, the critical part of the above sentence starts with If and leads to the question of what is the real world probability of getting 313 million Americans and the more than 30,500 counties and incorporated cities to make that great leap backward to 1950 in terms of energy use and carbon dioxide (CO2) production. Let’s start this inquiry with a number of social-cultural factors that influence judgments and decisions.

Social-Cultural Aspects of Pro-Environmental Behavior

Research over the past several decades in psychology (Weber and Stern 2011) has established evidence that indicates individual and collective decisions are more influenced by worldviews, values, and affective processes than they are by analytical processes, which are characterized by formal logic, mathematics, and probability (Weber 2006, 2010). As a pertinent example, risk perception research by Kahan et al. (2011 and 2012) determined that when scientific information conflicted with shared ideological values and beliefs (notably conservative political worldviews), those communally shared values were affirmed and the science was not. That situation may also be explained in part by the Theory of Cognitive Dissonance (Festinger 1957), wherein people will avoid information that causes feelings of uneasiness (dissonance) and add new “information” that is compatible with their existing belief system.

Critical to this discussion of pro-environmental actions are the roles political ideology and values play. McCright and Dunlap (2000), Dunlap and McCright (2008), and Dunlap and Jacques (2013) analyzed American denialist challenges to environmental problems. They determined that the disagreement stemmed from collaborative efforts by a powerful conservative political movement composed of right-wing foundations, think tanks, and environmental skeptics aligned with the Republican Party. McCright and Dunlap (2011) presented additional evidence that between 2001 and 2010 the views of the American public on environmental issues have become increasingly polarized along both partisan (Democrat versus Republican) and ideological (liberal versus conservative) positions. That evolution has certainly affected the way cities and urban planners operate with respect to environmental issues.

Another significant social-cultural problem that affects individuals, organizations, and cities is inertia, or the innate human resistance to change, especially to change that is interpreted by many as not in evidence but that is predicted or anticipated (Zárate et al. 2012). Naturally, cultural inertia affects institutions and political jurisdictions as well as individuals. As humans, we tend to value things with which we are familiar far more than things that are either unfamiliar or are not yet extant. As a result, we have cognitive biases against getting rid of things we should discard based on pure rationality, whether they are outmoded technology, ineffective politicians, or incorrect views of the future. It is not that people or jurisdictions are stupid or simply too lazy to change but that their actions are strongly influenced by a set of psychological short-cuts that our brains take without us realizing what is going on, short-cuts that make what is familiar and seen much more comforting and reassuring and difficult to dismiss than what is unfamiliar and unseen.

For large-scale organizational change to occur, some type of system-wide failure must overcome our innate cultural inertia and precipitate that transformation (Weick and Quinn 1999). In the case of climate change, if between 41 to 64 percent[2] of the U.S. population rejects scientific evidence that a system-wide failure—human caused global warming—has or will occur, then inertial resistance to the need for widespread socioeconomic change will be high. Many, if not most, Americans and local political jurisdictions are either comfortable with their present energy- and carbon-intensive lifestyles and operations to willingly change their environmental behaviors or their mindsets are too focused on ideologically-based skepticism (McCright and Dunlap 2003 and 2011) to accept scientific evidence that human caused failure of the climate system is here and appropriate action is required now if our culture, as we know it, is to survive.

A large number of ideological conservatives and right-wing organizations, as well as local political jurisdictions directly or indirectly influenced by conservatives, are convinced climate change, sustainability, New Urbanism, smart growth, livable cities, traditional neighborhood design, and related planning ideas are U.N. sponsored, liberal-socialist conspiracies designed to strip individuals of their property rights and their freedom.[3] If we eliminate those core conservatives from the universe of Americans who would voluntarily return to energy and material consumption patterns characteristic of 1950, that step removes a certain percent of the population and would allow an assessment of how many Americans would voluntarily change their lifestyles to produce less CO2. The question is how that percent can be calculated since this paper does not contain a sophisticated and expensive sampling procedure that was part of a national survey that asked appropriate questions.

To overcome that difficulty, I assume that Republican and Democratic Americans are proportional to the numbers of votes cast for Barack Obama and Mitt Romney in the 2012 Presidential Election and that independents are relatively equally split between both parties. I realize that assumption is not accurate but it provides a reasonable base from which to calculate percentages in the absence of more exact information. The results of recent national Gallup poll (Saad 2013) that examined concerns about global warming by political party are used to determine the percentage of Americans willing to decrease energy consumption. The poll found that 25 percent of Democrats and 60 percent of Republicans did not worry a great deal about global warming. Multiplying the numbers of Presidential votes cast by party by those percentages and adding the totals result in 41 percent of the total American population who would likely reject calls to reduce energy consumption and carbon production to 1950 levels. For purposes of this assessment, that group is labeled Core Conservatives #1.

Another part of that 2013 Gallup poll asked party members if they thought global warming was a serious threat in their lifetimes. Fifty percent of Democrats saw no threat as did 82 percent of Republicans. Multiplying the numbers of Presidential votes cast by party by those percentages and adding the totals result in slightly over 64 percent of Americans who do not worry about global warming. That group was labeled Core Conservatives #2. If we eliminate both sets of core conservatives from the universe of Americans who would voluntarily return to energy and material consumption patterns characteristic of 1950 to mitigate the adverse effects of climate change, that step removes somewhere between 41 percent and 64 percent of the population.

Another percent can be eliminated that would never entertain the thought of living in a non-air conditioned house containing only 983 square feet, which was the 1950 average, or consider basically throwing away their investment[4] in a large-lot single family suburban residence to move into a smaller home in a more densely populated city. Based on my experience as a practicing urban planner and knowing the size of the average new house in 2012 was about 2,500 square feet, that number might even be higher than 75 percent of the total population, especially if we include those who do not yet live in such a spacious residence but aspire to. If we assume two-thirds of that 75 percent is already accounted for in the previously cited 41 to 64 percent (since Republicans are more suburban-oriented than Democrats), we have somewhere between 66 to 89 percent of the population disinclined to leap backward into the future to mitigate the adverse effects of climate change.

Next, we have to consider that segment of the population that enjoys a low-density suburban lifestyle and would not willingly abandon it. Let’s assume that percent not already accounted for would equal five percent of the population (admittedly a guesstimate). The remaining 6 to 29 percent of the U.S. population constitutes a relatively small number of environmentally virtuous individuals on which to hang national hopes of averting potentially catastrophic effects of anthropogenic climate change.

Scale, Local Jurisdiction Governance, and Climate Change

Individual and jurisdictional pro-environmental behaviors typically involve multi-scalar and cross-boundary issues, e.g., CO2 produced in one jurisdiction or at a specific site does not remain within jurisdiction boundaries or at the local scale. Therefore, it makes sense to examine the climate change challenge from viewpoints familiar to all planners: geospatial scale (Sayre 2005; Wilbanks 2007) and governance.

Climate changes build collectively from micro-scales to the global scale (Wilbanks and Kates 1999), the largest organizational level with which humans deal, astronauts and astroscientists being exceptions to that generalization. But most people typically live the majority of their lives at much more constrained geospatial and temporal scales that are defined by personal action, which can range in geographic extent from as small as a homeless person’s shelter on the street to larger than the metropolitan areas in which much American life takes place. It should be evident that many hundreds of thousands or even millions of small-scale, voluntary pro-environmental actions by individual people, local political jurisdictions, and industries must coalesce to affect global conditions, which is obviously the case in terms of climate change.

On the global effects level, humans inject around 35 billion tons of CO2 into the atmosphere each year.[5] On the national level, about 5.3 billion tons of CO2 are produced annually in the U.S.,[6] which in 2012-2013 at the personal level of detail means each American is responsible for producing about 17 tons of CO2. Based on information developed by the Carbon Dioxide Information Analysis Center of the U.S. Department of Energy, CO2 use by Americans doubled from 1950 to the present (Borden et al. 2011).

If we stay on the national level scale, we have to consider what has happened in terms of CO2 emissions in the U.S. from 1950 to the present. Over that interval, the U.S. share of global emissions has declined from 44 percent to about 15 percent, a paper decline largely due to increasingly higher production of carbon by non-Western countries—e.g. China and India—as well as a recent slight actual decrease in carbon use by Americans, which is probably due to power generating plants switching from coal to natural gas.[7] The obvious question is, if individuals in developing countries like China and India, are rapidly increasing CO2 production, which they are, what global benefit would result if between six and 29 percent of the U.S. population drastically changed their lifestyles and cut their CO2 production in half? The answer should be obvious.

In terms of pro-environmental decision-making associated with local scale, those of site and local political jurisdictions, widespread change initiated by individual jurisdictions as well as by coordinated and collaborative cross-boundary pro-environmental behavior or governance also seems problematic. A number of reasons have been advanced by planners for the failure of local political jurisdictions to adopt more environmentally responsible plans in terms of smart growth, sustainability, or ecological planning, which I regard herein as surrogates for mitigating the adverse effects of climate change.

When opportunities in U.S. cities were examined for obstacles to climate change mitigation using the example of the Cities for Climate Protection Program, Betsill (2001) found that institutional barriers—such as inappropriate bureaucratic structure, lack of administrative capacity, and budgetary constraints—made it difficult for municipalities to implement targeted policies and actions. The question her research raised was whether local initiatives could make meaningful contributions to climate change mitigation in the absence of substantive governance changes at the state and national levels; for similar conclusions, see McCann (2003).

Downs (2005) addressed the issue as to why few cities have adopted smart growth principles. His research centered on numerous practical difficulties in changing long-established powers and authority of local government as well as in changing, in a short time period, existing cultural preferences—such as residential land use patterns characterized by low-density and high demand for vehicular transportation. Much like Betsill, Downs argued that the political resistance at state and local levels to such changes would be extraordinarily difficult to overcome.

Analysis of barriers to the adoption of urban-ecological planning techniques by Berke (2007) provided several observations pertinent to governance similar to those proposed by Betsill and Downs, particularly that local governments have built-in difficulties that hinder such adoption. One specific problem Berke (2007, p. 68) raised is that the level of detail required by local governments in gathering data that would be incorporated into traditional planning tools is inadequate for ecological management, which requires far more detailed and complex information. Another, even more critical barrier Berke identified was the spatial mismatch between the local scale characteristic of non-state political jurisdictions and the regional to national scale of ecological issues (including climate change mitigation), making multi-scalar and cross-boundary relationships very difficult to address in an ecologically sound manner, especially since local American government is not structured to deal with multi-level decision-making challenges, a conclusion shared by Betsill (2001) and Downs (2005).

Other research on key challenges concerning the powers of local government and conflicts between local goals for economic development and climate change mitigation have demonstrated the restricted ability of local actions to affect climate change (Bulkeley and Betsill 2003). Related research focused on environmental issues in England, including sustainability and climate change mitigation, found that forms of governance required to address those issues stretched across geographical scales and beyond urban boundaries (Bulkeley and Betsill 2005, 42). They argued that the ‘urban’ governance of climate protection involved “relations between levels of the state and new network spheres of authority which challenge traditional distinctions between local, national and global environmental politics.” When Betsill and Bulkeley (2006) analyzed how U.S. cities in the Cities for Climate Protection (CCP) Program might be conceptualized as part of global environmental governance, they found that only by taking a multi-level, multi-scalar perspective could the social, political, and economic processes that shape global environmental governance be captured.

Research in the U.K. by Wilson (2006) addressed the difficulties of adopting spatial planning policies at the local level in terms of mitigating or adapting to climate change. She determined that, other than the issue of climate change’s contributions to local flood risk, the wider implications for biodiversity and water resources are not yet integrated into plans. She attributed that failure to a “lack of political support and lack of engagement of the planning profession with climate change networks” (Wilson 2006, 609). But she also pointed to local level difficulties in acknowledging the need to react to climate change, stemming in part from the relatively short-term perspectives of local plans being out of sync with the long-term implications of climate change, a governance issue similar to those raised by Betsill (2001), Downs (2005), Bulkeley and Betsill (2005), and Berke (2007).

Although relatively few U.S. cities have adopted specific climate change action plans, Tang et al. (2010) examined 40 such plans in terms of local jurisdictional efforts to mitigate climate change. Their study focused on plan quality as expressed through local awareness and analysis that led to actions. Tang and colleagues found high levels of climate change awareness, moderate levels of analysis, but limited action approaches, part of which the authors attribute to the lack of enabling legislation or directives generated by state government that would put pressure on local jurisdictions to enact effective mitigation policies and implementation measures, another governance issue.

Perhaps the best summation of the present situation with respect to climate change governance is provided by Shove (2010, 1283), when she writes: “. . . that [climate change] policy, as currently constructed, is necessarily incapable of conceptualizing transformation in the fabric of daily life on the scale and at the rate required.”

Remarks

This paper began by considering the possibility of most individual Americans and local political jurisdictions leaping backward into the future in terms of energy and carbon use. After some examination it seems that possibility is unlikely unless pro-environmental behaviors on the part of cities and counties, commercial and industrial firms, and the general population are mandated and enforced through new federal policies, laws, and regulations. Short of the U.S. being transformed into the type of command and control political-economic system in existence during World War II (Delina and Diesendorf 2013), it seems unlikely that voluntary actions on the part of individual Americans who are environmentally virtuous could play a significant role in the national or global reduction of carbon.

The reality is the U.S. and other developed nations have sufficient time to avert the worst effects of climate change if they desire (Hale 2010). A necessary condition for that to happen is the populations of those nations must generate the political will to demand that national and international policies be adopted and laws and regulations put in place at all levels of political jurisdiction to ensure climate change mitigation measures are implemented within a very short time period.

Practicing planners are perfectly positioned in that nested jurisdictional hierarchy because the majority of the individual phenomena that underlie environmental processes, resource use, economic activities, population dynamics, and climate change arise at site and local scales (Wilbanks and Kates 1999). The two central challenges in terms of the success of global climate change strategies is controlling local scale emissions and initiating effective mitigation/adaptation policies and actions locally. As Wilbanks (2007, 286) has succinctly pointed out: “Scale matters most because it is directly related to how and where governance decisions are made that affect sustainable development.”

The question then arises as to what practicing planners, whose work is predominantly at the local scale, can do to help stimulate changes at various levels of government that address climate change mitigation. Although the answer is complex I believe planners are well positioned to apply lessons learned from exemplars like Rosa Parks, Rachael Carson, Arthur Marshall and Marjory Stoneman Douglas, and Marjorie Carr, Jack Ohanian, and David Anthony. All were activists who struggled against daunting odds and succeeded in ways no one anticipated. Rosa Parks changed the way Americans understood the battle for human dignity and civil rights (Williams 2002). Nearly single-handedly, Rachael Carson (1962) changed our collective perception of the use of hazardous chemicals in the environment. Arthur Marshall and Marjory Stoneman Douglas fought for decades and were able to save the Everglades from total destruction (Grunwald 2006). And Marjorie Carr, Jack Ohanian, and David Anthony created a grassroots movement that defeated the Cross Florida Barge Canal despite facing staggeringly powerful opposition from the federal government and the State of Florida as well as from wealthy and politically connected canal supporters (Noll and Tegeder 2009).

The combination of highly motivated individuals, determined non-governmental organizations, credible evidence complied by scientists, and sympathetic political leaders at every decision-making level can result in positive change. It is a lesson no one who is concerned about the environment can afford to forget. Research by Chawla and Cushing (2007, 438) demonstrated that lesson is reality-based and not wistful thinking. Their analysis of the world’s most serious environmental problems suggested that the effect of private actions is limited unless they are combined with organizing for collective public change. Although many practicing planners are highly skilled at public organization, the question is whether they, local political jurisdictions, individuals, NGOs, and other stakeholders are sufficiently motivated to act decisively now.

The questions posed by Bulkeley and Betsill (2003 and 2005), Downs (2005), Wilson (2006), and Berke (2007) concerning how the political structure of cities affects pro-environmental behavior raises even more daunting issues. Changes in governance and administrative behavior, especially those that are multi-scalar and cross-boundary in nature, are always difficult. Making those changes in a relatively short time period is even more so, especially if the involved political jurisdictions currently exhibit a nested, hierarchical structure that may need to experience transition (Shove and Walker 2007).

Although for reasons detailed above I remain pessimistic about meaningful reductions in CO2 tonnages occurring in time to avoid potentially catastrophic effects on the world economy and on civilization as a whole, I firmly believe that targeted and coordinated actions by planners, cities, and committed individuals and organizations still have the possibility of success. However, due to the ever increasing rate humans are injecting CO2 into the atmosphere, the time available to achieve positive outcomes in terms of climate change mitigation is limited.

References

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Betsill, Michele M. 2001. “Mitigating Climate Change in US Cities: Opportunities and Obstacles.” Local Environment: The International Journal of Justice and Sustainability 6, 4: 393-406.

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Festinger, Leon. 1957. A Theory of Cognitive Dissonance. Stanford, CA: Stanford University Press.

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Weber, Elke U. 2006. “Experience-Based and Description-Based Perceptions of Long-Term Risk: Why Global Warming Does Not Scare Us (Yet).” Climatic Change 77, 1-2: 103-120.

Weber, Elke U. 2010. “What shapes perceptions of climate change?” Wiley Interdisciplinary Reviews: Climate Change 1, May/June: 332-342. Accessed May 17, 2013 at http://wiki.cbr.washington.edu/qerm/sites/qerm/images/8/8d/Weber2010.pdf

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Notes
[1] Most atmospheric scientists, the European Union, and the State of California advocate setting a target for industrialized nations of achieving an 80 percent reduction in greenhouse gases, based on 1990 levels, by 2050 in order to stabilize CO2 concentrations at about 450 ppm by 2050. Although I applaud that ambitious target, for purposes of this paper I believe it is more pragmatic for the U.S. to use a 50 percent reduction by 2050 as our hypothetical goal.
[2] See calculations on p. 5.
[3] For two informal, subjective, but well researched descriptions of this situation, see Flint (2011) and Mencimer (2011).
[4] I use the term “throwing away” since few buyers would be willing to risk purchasing such a residence or would offer to purchase it at such a reduced price that re-investment in another residence would be problematic.
[5] http://edgar.jrc.ec.europa.eu/overview.php?v=CO2ts1990-2011 
[6] http://edgar.jrc.ec.europa.eu/overview.php?v=CO2ts_pc1990-2011
[7] See The Economist. “America's falling carbon-dioxide emissions: Some fracking good news.” May 25th 2012: http://www.economist.com/blogs/schumpeter/2012/05/americas-falling-carbon-dioxide-emissions

Moving Beyond Conventional Environmental Planning

By Robert Ernst and Jerry Weitz, FAICP

Note: this post is a version of an article published in the journal, Practicing Planner, in Spring 2013.

Researchers have documented numerous examples of the lack of broad-based commitment by planners to practice a more responsible environmentalism in cities throughout the United States and Canada (Brody and Highfield 2005; Tomalty 2009; Stevens et al. 2010; Garde et al. 2010). A key challenge for practicing planners is to create cities that are not compartmentalized from the environment. When planners propose to protect the environment, the most common response has been to apply conventional planning tools and processes: inventory the resources, pose policies to protect them, seek community acceptance, get local elected officials to adopt the policies in a comprehensive plan, and then implement the plan and policies with regulations, programs, and other actions.

The conventional approach to environmental planning has not functioned adequately for several decades. Communities, as served by planners, have not arrived at the desired end state of urbanization that is respectful of, and even enhances, the environment. Certainly part of the failure to achieve our environmental aims can be attributed to planners. In this essay we identify some possible reasons why we have not reached that end, and we speculate about what planners might do differently to reach the desired end of environmentally responsible land development and urbanization.

Target Refocusing: Creating Better Cities

Systemic landscape changes, such as habitat destruction and loss of biodiversity, are typically triggered by individual and coalescing local actions, such as cities built and operated as if they were completely unrelated to the environment. In North America, that topic has occupied the attention of many practicing urban planners (Campbell 1996). However, that focus on making cities more functional does not mean all or even most practicing planners are actively pursuing environmentally responsible urbanization, despite its having gained the status of an international “best practice” as New Urbanism, smart growth, sustainability, and ecological cities (World Urban Forum 2006; United Nations 2007).

Although many practicing planners are in the process of developing local and site scale solutions to the challenge of creating cities that are not compartmentalized from the environment, when North American planners as a whole are considered that movement seems to be in the initial stages (Saha and Paterson 2008; Upadhyay and Brinkmann 2010). A detailed survey by Brody et al. (2010, 591) of more than 1,500 agency personnel from key state, regional, and local agencies and interest groups involved in climate change policy and actions found that those agencies “were not engaged in climate change policy, nor is the issue on their agendas.” The study also determined that, for local and state decision-makers, climate change issues (including more environmentally responsible cities) were of low-priority.

Since the adverse effects of irresponsible urbanization and climate change are interrelated, the 2010 Brody study raises questions as to how to engage local decision-makers in needed urban-environmental change. A number of other studies (Brody 2003a; Tang et al. 2011; Brody et al. 2012) suggest specific techniques—education, ecological values, and targeted stakeholder participation—may successfully involve individuals and decision-makers in actions that result in more responsible urbanization. Since planners deal with socioeconomic and environmental variables and public education-outreach as a normal part of their professional responsibilities, they are perfectly positioned to address responsible urbanization at critically important local and site scales where almost all landscape change necessarily begins (Wilbanks 2003, 2006). Practicing planners need to actively pursue environmentally responsible urbanization and development at the site, local, and regional scales, where we can be most effective. The goal is to make existing tools more accessible to planners so that better cities and more responsible urban development may result from their application (Brody 2003b).

Assess Before Participation and Planning

It should come as no surprise to experienced planners, but any effort to arrive at policies and programs that improve settlement patterns in relation to the environment must begin with appropriate assessments. Planners should complete a detailed resource inventory establishing ecosystem zones, habitats, boundaries, functions, biodiversity of wildlife and vegetation species, land cover, soils types, geological-topographic features, natural and human-caused hazard areas, climate/micro-climates, watersheds, floodplains and wetlands, lake or marine resources, groundwater recharge areas, and dedicated conservation property and its ownership-management status.

Because natural resources and environmental challenges span local boundaries and regions, planners should invite other governmental jurisdictions to participate in the preparation of a shared, jointly maintained natural resource database using GIS. Where feasible to do so, the locality or region should partner adjacent political jurisdictions, as well as with businesses and institutions, to complete the inventory.

The assessment of natural resources and environmental impacts resulting from urbanization and land development must be completed prior to engaging in the planning process. If environmental inventories and assessments come during planning instead of before the process has started, the findings that enlighten planners and the public may be manifested too late to be fully appreciated and implemented.

Assessing the current situation regarding the urban-environment nexus should include a self-assessment by planning staff to identify the full range of adverse human effects urbanization and land development have on natural resources and the environment. A key to completing this step successfully is to identify interconnections between urban socioeconomic factors and the natural environmental resource system. We recommend that planners issue a “State of the City” report that clearly highlights the effects of urbanization on the environment. Before initiating a process of creating a plan, planners should formally request that the governing council adopt by resolution the findings in the State of the City report about how certain urbanization practices adversely affect the environment.

As a part of the State of the City report, or in a separate work product, planners should also identify best practices used in other communities (policies, regulations, programs, actions, and other measures) to mitigate adverse land development impacts on the environment and determine their potential applicability locally or regionally. Ultimately, planners will propose an initial set of guiding principles articulating what it means to be a better city in terms of the environment. Before publishing those potential best practices, however, planners must examine them for conflicts. Where conflicts exist, the principles must be revisedor otherwise reconciled. Hence, it is important that planners use the resource inventory to set objectives and priorities and identify management-action alternatives for each significant resource area.

Involving Elected Officials First, Not Last

Many public planning processes begin with appointment of a task force or steering committee that makes recommendations that ultimately do not gain the support of local elected officials. If that hasn’t happened in your community, you’ve seen or heard about it occurring in other localities. Perhaps planners should start with the jurisdiction’s political leaders, who must ultimately approve and implement new approaches and initiatives. This suggestion doesn’t mean planners should draft plans in consultation only with elected officials, but that some preliminary “buy in” to the process and discussion of likely policy outcomes (including actions) need to be established and firmly grounded before engaging in more inclusive planning processes.

Participation and Consensus Building in the Pursuit of Shared Values

It may be that we are failing to achieve better urban-environmental relationships because we are not executing appropriate citizen-stakeholder participation processes. Serious questions should be raised as to how to we engage local decision-makers, stakeholders, and citizens in effectuating needed urban-environmental change.

As planners, we know what we want to achieve in any participation program. So we imagine the jurisdiction’s future where the quality of life is enhanced for all. We create a vision statement, and we explore the full range of possibilities for achieving that vision. We seek participatory processes that are authentic, genuine, open, welcoming, transparent, and responsive to citizen needs and expectations. Planners want participants to gain ownership in the planning process and resulting product. Ideally, we want ideas, concepts, goals, and principles to bubble up from the hearts and minds of participants, rather than have them handed down from decision-makers. This desire may lead us to overlook the important power that elected officials have and will exercise during the process, usually at the end when asked to adopt a plan and implementing measures.

While not intentional, planners often overlook existing community networks or at least fail to capitalize on them during the participation and planning process. To be successful, we must determine the strength and nature of existing community networks and develop effective strategies to mitigate or minimize weaknesses and constraints in those networks. This would put planners into a role of consensus building and policy advocacy prior to full engagement of the community in the planning process. Ethics of the planning profession require us to engage populations not ordinarily active in jurisdictional affairs, especially minorities and lower income groups and individuals that may have reduced confidence in their ability to influence jurisdiction decisions.

Success depends on building the social capacity and public will to address real world environmental challenges. Planners sometimes use politically charged terminology such as the word, “sustainability.” We need to approach environmental problems in ways that avoid politically charged terminology and focus on shared communal values to achieve progress.

We must employ education and citizen involvement programs to arrive at those shared environmental values. Planners need to motivate our community members to pursue substantive changes to urbanization so it occurs in an ecologically beneficial way. We are not succeeding, in part, because we aren’t using all of the citizen participation and consensus building approaches at our disposal. We can improve our participation processes by addressing pre-conceptions and hidden agendas up front, and by soliciting statements of perspectives and experiences from participants. Again, the goal is to create a shared understanding about what it means to create a more environmentally friendly city.

We anticipate that planners will respond to our advice as “easier said than done.” It may be that to get to shared environmental values that planners must first conduct training workshops on urban-ecological relationships and strategies for improving those relationships. We must identify environmental values people of all political persuasions share and can support. These may include saving money by cutting energy and infrastructure costs, breathing fresh outdoor air, swimming in clean water, catching fish that aren’t laced with chemical poisons, bringing back wildlife diversity, restoring wetlands and riparian systems, and improving urban parks. Success may require providing opportunities for community groups and individuals that involve meaningful environmental improvement and restoration opportunities within the jurisdiction.

Revisit the Planning Toolbox

Not all planners are able to grasp the extent to which ecosystem science has informed us about how urbanization affects the environment. Further, planners may be overlooking the basic tools that can be employed to achieve more environmentally responsible urbanization. Quite a few toolboxes or toolkits are available for planners interested in contemporary urban environmental or sustainability initiatives (see Brody 2003b for an illustrative list). However, most of those toolboxes have not resulted in a meaningful integration of urban planning with ecosystem science.

We encourage planners not to overlook the conventional tools of environmental policy implementation: cost-benefit analysis to determine scheduling and budgeting parameters; capital improvement programming; planned unit developments, purchase and/or transfer of development rights programs, urban growth boundaries, landscape ecological principles of land use planning and design, mitigation banking, density incentives for compact development and clustered housing, stormwater management ordinances, low-impact development practice guidebooks, habitat and damaged ecosystem restoration projects, critical area overlay districts and ordinances, energy savings awareness campaigns, urban forestry management, intergovernmental agreements for protecting natural areas crossing jurisdictional boundaries, and many others.

Inadequate Implementation and Monitoring

Planners are undoubtedly skilled at directing our communities as to how to implement plans. But we suggest that planners have not spent enough time tying policies and implementation measures together before the policies are adopted. In suggesting environmentally responsible policy, it must be evident to planning process participants and decision-makers what policy effectuation means in terms of regulations and implementation measures. It is insufficient to propose policies without at least presenting tentative or interim schedules and budgets for the actions needed to implement the policy. And, it is not enough to suggest implementations and set out a tentative schedule. There must be mechanisms for reviewing progress. Milestones for every six months of the implementation phase should be articulated. Progress should be reported annually. The resulting plan must inform and guide policy decisions and operations at all levels of local government.

Conclusion

The goal of creating better cities is for political jurisdictions to be able to plan, design, and construct urban development so the environment is not typically altered, degraded, and even, in all too many cases, destroyed. That goal includes making the idea of a better city and region directly relevant to the public and to a full palate of stakeholders. In this essay, we have identified some of the reasons planners may not be attaining the goal of environmentally responsible urbanization and land development. In review, we recommend a refocusing on regional and local environmental problems. We urge the completion of environmental assessments prior to engaging in the planning process itself, and we suggest articulating non-conflicting principles and their most likely policy implementation measures to implement those principles. We suggest that elected officials should be apprised of those measures, and that they should buy into the process, before broader participation processes are undertaken. Participation processes have not but should emphasize identifying shared environmental values. We also urge planners not to overlook the obvious but growing toolbox of implementation measures that can help mitigate the environmental impacts of urbanization and land development. We also suggest greater attention to connecting policy and implementation and inclusion of monitoring techniques.

The primary advantage of the process outlined in this essay is that it focuses on building the social capacity and public will to address real world environmental, social, and economic challenges at local scales in a scientifically valid manner and is not limited to simply constructing more efficient urban socioeconomic infrastructure. Its coordinated approach links planning tools and incentives that integrate socioeconomic and environmental objectives in the context of local community involvement.

Leading effectively toward a more socially just, economically sustainable, and environmentally responsible future is like walking gingerly through a mine field of conflicting positions and opinions. But that complex skill is one planners must quickly come to perfect (Jepson and Edwards 2010) if we are to make a significant difference in terms of more responsible urbanization and land development.

Brief Bios

Robert Ernst has a PhD in Geography from the University of Florida and is a specialist in land-based systems, including comprehensive urban and regional planning, policy/strategic planning, economic development, land use, and environmental impact studies. His nearly 40 years’ practical experience includes managing large-scale assignments involving multi-disciplinary teams and devising and implementing public involvement strategies. He has provided consulting services to local political jurisdictions; regional, state, and federal agencies; foreign governmental agencies; and private land development and natural resource firms in the United States and overseas. Ernst recently retired and lives with his wife in the St. Louis metropolitan area.

Jerry Weitz, PhD, FAICP, is editor of Practicing Planner. He is an associate professor and director of the urban and regional planning program at East Carolina University and a planning and zoning commissioner for Greenville, North Carolina.

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