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Missing the Warning Signs? The Case of “Yellow Air Day” Advisories in Northern Utah

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Abstract

Using a dataset consisting of daily vehicle trips, \(PM_{2.5}\) concentrations, and a host of climactic control variables, we test the hypothesis that “yellow air day advisories” issued by the Utah Division of Air Quality resulted in subsequent reductions in vehicle trips taken during northern Utah’s winter-inversion seasons in the early 2000 s. Winter inversions occur in northern Utah when \(PM_{2.5}\) concentrations (derived mainly from vehicle emissions) become trapped in the lower atmosphere, leading to unhealthy air quality over a span of time known colloquially as “red air day episodes”. When concentrations rise above 15 \(\upmu \textrm{g}/\textrm{m}^3\) toward the National Ambient Air Quality Standard average daily threshold of 35 \(\upmu \textrm{g}/\textrm{m}^3\), residents are informed via different media sources and road signage that the region is experiencing a yellow air day, and are urged to reduce their vehicle usage during the day. Our results suggest that the advisories have provided at best weak, at worst perverse, incentives for reducing vehicle usage on yellow air days and ultimately for mitigating the occurrence of red air day episodes during northern Utah’s winter inversion seasons.

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Fig. 1

Source https://onlinelibrary.utah.gov/utah/counties/ and https://www.freeworldmaps.net/united-states/utah/location.html

Fig. 2

Source Moscardini and Caplan (2017)

Fig. 3

Source Moscardini and Caplan (2017)

Fig. 4

Source Moscardini and Caplan (2017)

Fig. 5

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Notes

  1. In their systematic review of the ecolabeling literature, Potter et al. (2021) conclude that ecolabels help motivate consumers to choose greener products. Experimental evidence from Rihn et al. (2019) suggests that ecolabel format (i.e., text vs. logo) influences consumers’ visual attention and, concomitantly, product valuation. Logos capture relatively more visual attention than text ecolabels, which in turn increases respondents’ willingness to pay for ecolabeled products. Shumacher (2010) finds that demand for ecolabeled goods is higher among environmentally conscious consumers than price-oriented consumers. Kaiser and Edwards-Jones (2006) caution that a myriad of issues bedevil the impact of ecolabeling in marine fisheries, issues pertaining to a general lack of consumer concern for marine fishes and sustainable fisheries, the absence of guaranteed, continued financial benefits to participating fishers, and difficulties associated with quality assurance (i.e., compliance of marine fisheries).

  2. Hamilton (1995) was the first to show that firms self-reporting their toxic emissions via the U.S. Environmental Protection Agency’s (EPA’s) Toxic Release Inventory (TRI) experienced abnormally negative returns on the day the information was first publicly released. With respect to actual firm-level emissions in response to the TRI, Terry and Yandle (1997) find that, all else equal, lower per-capita emissions levels were recorded in more densely populated areas of the country. According to de Marchi and Hamilton (2006), subsequent decreases in self-reported emissions were not always matched by similar reductions measured via EPA monitors. With respect to the control of nonpoint source water pollution, Ribaudo and Horan (1999) find that favorable conditions for information dissemination exist when (1) actions that improve water quality also increase firm profitability, (2) firms have strong altruistic or stewardship motives to begin with, or (3) the on-farm costs of water quality impairments are sufficiently large. However, none of these three conditions guarantees an expected improvement in water quality.

  3. Similar to Tribby et al. (2013) and Cummings and Walker’s (2000), Utah’s advisories were disseminated “day of”, and hence were not as peremptory as “day-before” advisories would otherwise have been. We nevertheless test for the existence of potential day-before effects in Sect. 6, as their existence in our data would suggest that vehicle users base their decisions on expectations that an advisory will be issued, e.g., in response to an evening news report on the radio or television that predicts ensuing poor air quality, or information on current \(PM_{2.5}\) concentrations available from various websites.

  4. Noonan (2011) argues that air quality advisories can impact behavior, mostly among sensitive groups such as the elderly, and for high-exposure activities, such as outdoor exercise. In other words, advisory programs do not uniformly alter a given population’s behavior. Impacts vary across individuals, contexts, and activities. In fact, some of these behavioral impacts may be perverse, e.g., by inducing a greater reliance on automobiles on alert days in order to reduce one’s exposure to poor air quality. Hence, advisory programs can instigate tension between an individual’s altruistic impulses to mitigate his or her contribution to the air quality problem by reducing vehicle usage versus the perceived need to reduce the immediate health risks associated with the problem by increasing vehicle usage. As pointed out by an anonymous reviewer, the degree of this tension likely depends upon a pollutant’s concentration level, i.e., the extent to which the local environment is polluted.

  5. Cutter and Neidell (2009) point out that Welch et al.’s. (2005) standard errors were not adjusted to account for observing multiple stations per hour per day, and are therefore likely under-estimated.

  6. Cummings and Walker’s (2000) finding was later echoed by Henry and Gordon’s (2003) analysis of telephone survey responses from Atlanta residents.

  7. Moser and Bamberg (2008) estimate an 11% reduction across 141 studies spanning workplace travel plans, school travel plans, and travel awareness campaigns.

  8. As Rivera (2021) points out, by the time of her study the implementation of mandatory driving restrictions based upon license plate numbers had become a common regulatory strategy used worldwide to improve local air quality conditions and reduce traffic congestion. See Barahona et al. (2020) and Bonilla (2019) for recent studies on mandatory driving bans, and Caplan and Kim (2018), and references therein, for earlier studies.

  9. This result is perhaps the most widely cited finding in the literature. More recently, Zoe (2021) finds that “pollution gaps”, which exist in areas of the US where pollution concentrations are measured intermittently by regulatory authorities (in specific, once every six days of the week), are excerbated when advisories accompany relatively high concentrations on days during which the concentrations are measured, i.e., on “on-days”. Pollution gaps occur when, all else equal, concentrations are lower on on-days than “off-days”, i.e., days when concentrations are not measured by regulatory authorities (but are measured by the researcher using satellite data). Zou’s empirical model detects 1.6% less particulate pollution during on-days than off-days. Further, there is a 10% higher likelihood that an advisory is issued on on-days, and the advisories are associated with pollution gaps of 5–7% (as compared with the average 1.6% gap). This evidence leads Zou (2021) to conclude that gaming among regulatory authorities most likely reflects short-term cutbacks of polluting activities during critical times, e.g., when a county’s noncompliance risk is high. Advisories are used strategically by the authorities, thus widening the pollution gap.

  10. Cutter and Neidell’s (2009) evidence supports the former condition, i.e., that unobservable factors do not vary around the trigger concentration level. See Lee and Lemieux (2010) for a survey of the RD method.

  11. In a series of robustness checks, Saberian et al. (2017) find a roughly 40% reduction in the response of leisure cyclists due to alert fatigue, compared with only a 20% response reduction in commuter cycling. The authors caution that because the number of consecutive-day alerts in their data is minimal—occurring only seven times during the five-year study period—the precision of their alert-fatigue estimate is concomitantly diminished. As described in Sect. 6, the number of consecutive-day alerts in our data is markedly higher than Saberian et al.’s.

  12. In other words, bushfire activity satisfies the exclusion restriction (c.f., Angrist et al. 1996).

  13. Similar to Cache Valley (northern Utah’s main county), Salt Lake and Davis counties were in non-compliance with the NAAQS for \(PM_{2.5}\) concentrations, as well as for ozone concentrations, during their study period.

  14. Although Rivera's (2021) findings align with Cutter and Neidell’s (2009), recall that Santiago’s advisory system is linked with varying stages of mandatory vehicle restrictions. When deteriorating air quality is less severe (and thus an initial alert is issued), temporary driving restrictions prohibit the driving of light-duty cars between 7:30 am and 9 pm. These temporary restrictions (applied discriminantly based upon license plate numbers) affect both clean and dirty vehicles (which are distinguished via green stickers affixed to the bumpers of the former type of vehicle) on any day of the week. As air quality deteriorates further, to a “pre-emergency” state, more dirty cars are banned permanently (until air quality improves) and more restrictions are placed upon the use of cleans cars. Under more adverse conditions, classified as “emergencies”, bans and restictions on both types of vehicles increase further. Santiago’s alert program does not rely upon voluntary self-restrictions, unlike the San Francisco Bay and Wasatch Front programs, as well as the program reported on here for northern Utah.

  15. Logan is the region’s largest city, with a population in 2009 (the middle of our study period) of 46,000 people residing in 16,000 households (Census Bureau, 2010). Cache Valley’s population is growing rapidly—it is expected to roughly double in size from 135,000 currently to 230,000 by 2050 (Perlich et al. 2017).

  16. Moscardini and Caplan (2017), Caplan and Acharya (2019), Acharya and Caplan (2020), and references therein elaborate on the precursors, causes, and patterns of elevated \(PM_{2.5}\) concentrations in Cache valley during the winter inversion seasons of our study period.

  17. There is only one instance in the dataset where a red air day episode occurred without having been preceeded by a yellow air day advisory.

  18. The positive link between vehicle usage and \(PM_{2.5}\) concentrations is certainly not unique to Cache Valley, Utah. For example, see Chen et al. (2020).

  19. In terms of commuting to work, slightly over 75% of northern Utah workers are estimated to drive alone to work, with another 11% carpooling and slightly less than 2% using public transport. The average one-way commute time is approximately 17 min. Approximately 64% of northern Utah commuters commute within the region (LSC Transportation Consultants 2017).

  20. Because individuals are assumed mypoic, our model is precluded from explicitly accounting for behavioral determinants of intra-seasonal alert fatigue among individuals. Nevertheless, if we assume that alert fatigue impacts equally each of the three types of individuals described below, then relatively speaking, the differences in individuals’ behaviors identified by the model would be unaltered in the presence of fatigue.

  21. The experimental literature is chockfull of studies where participants behave altruistically under certain conditions. For examples, see Fehr and Schmidt (1999), Bolton and Ockenfels (2000), Andreoni and Miller (2002), Andreoni and Rao (2011).

  22. An alternative theory could instead base individuals’ vehicle-use decisions upon their subjective risk preferences concerning their own personal health. These differences could be modeled in a context of what the current model identifies as either a Case 1 or Case 2 individual, i.e., an individual who either completely ignores his own contribution to the region’s PM2.5 concentrations via his vehicle usage, or who ignores his contribution to everyone else’s damages. In other words, the risk-preference model would consist of non-altruistic individuals who are distinguished instead by their subjective risk preferences. In this framework, individuals who perceive relatively high risk to their personal health associated with the issuance of an advisory would be more likely to increase their vehicle usage in response to the advisory. In contrast, those who perceive relatively low risk associated with the issuance of an advisory would be more likely to decrease their vehicle usage. Hence, although there is a different interpretation of what motivates individual responses to an advisory – altruistic tendencies versus subjective risk preferences—there is a consistency in terms of what characterizes the response at a regional level. In the case of subjective risk preferences, the region-wide response depends upon the proportion of low-versus high-risk individuals in the population.

  23. We again acknowledge that the effect of the advisory on vehicle usage in northern Utah is also averaged over commuting and discretionary trips. As Cutter and Neidell’s (2009) point out, commuters generally have little flexibility when it comes to missing a work day, especially if telecommuting alternatives are limited. Hence, commuting trips have a significantly higher cost of cancellation and thus are much less likely to be delayed or substituted away from than are discretionary trips.

  24. Station 490050004 was subsequently moved five miles north of downtown Logan to the town of Smithfield shortly after the conclusion of our study period.

  25. Average daily readings for atmospheric pressure were also obtained, however this variable was consistently statistically insignificant in the regressions presented in Sect. 5.

  26. The negative value for \(TempDiff_t\) indicates that the average day during our study period did not experience a temperature inversion.

  27. Tribbey et al. (2013) removed holidays from their data, thus eliminating their possible influence on individual’s vehicle usage. In contrast, we explicitly control for their possible effects.

  28. Although relatively low in magnitude—the Pearson’s correlation coefficients hover in the neighborhood of \(-\) 0.15 for each pairwise comparison—they are each statistically different at the 5% level of significance.

  29. We also estimated the model using a three-day forward moving average of \(VehicleTrips_t\) and found the results to be qualitatively similar to those for levels. The results using this specification are available from the author upon request.

  30. Stata/IC version 16.1 for Windows (64-bit x86-64) was used for all regression analyses reported in the paper.

  31. In other words, second-order autocorrelation is controlled for once three lags of \(VehicleTrips_t\) and two lags of \(Ln(VehicleTrips)_t\) are included as regressors in their respective models.

  32. Residual plots also indicate the existence of white-noise error terms at the respective lags. The plots are available upon request from the author.

  33. To test whether dummying for weekdays (\(=1\) if a weekday, 0 otherwise) rather than \(NotSunday_t\) is more appropriate, we conducted a series of means tests (assuming both paired and unpaired data). The results support what eyeballing the median and mean values of vehicle trip counts for each respective day of the week would suggest. The median and mean values reveal a starkly lower trip count for Sundays (20,030 and 19,553, respectively) vis-a-vis every other day of the week than do Saturdays (32,432 and 31,498, respectively). The means tests reveal strongly negative, statistically significant differences (p-value = 0.000) between mean vehicle trip counts on Sunday versus each day of the week, including Saturday. Saturday’s mean trip count is not statistically different than Tuesday’s, Wednesday’s, and Thursday’s. It is statistically larger than Monday’s (p-value = 0.032) and statistically lower than Friday’s (p-value = 0.000). Thus, there is some statistical justification to report the results for models including the NotSunday dummy variable rather than a weekday dummy.

  34. First-differencing also mitigates potential collinearity between the weather variables and one-day lags in our two advisory measures, as well as these measures each interacted with \(NotSunday_t\).

  35. The coefficient estimates corresponding to the two lagged \(Ln(VehicleTrips)_t\) variables included in these and all ensuing regressions to control for first- and second-order autocorrelation are not shown in order to eliminate unnecessary detail in the tables.

  36. We also ran the \(YellowAdvisory_t\) and \(YellowAdvisoryPlus1_t\) models with NotSunday broken out by specific day-of-the-week in order to trace the non-Sunday effect to any specific days. As expected, both models report statistically significant positive coefficients for each day of the week relative to Sundays. Results for the year dummy variables and the set of weather variables are qualitatively similar to those reported in Table 4. Both models also report positive coefficients for contemporaneous advisories issued on holidays and lagged advisories generally, although the lagged coefficient for \(YellowAdvisoryPlus1_t\) is statistically insignificant. Advisories interacted with specific (non-Sunday) days of the week are each negative but statistically insignificant in the \(YellowAdvisory_t\) model. The interaction term for Tuesday is significant in the \(YellowAdvisoryPlus1_t\) model. Again, the AIC and BIC values indicate that the \(YellowAdvisoryPlus1_t\) model better explains the data.

  37. These full set of results is available from the author upon request.

  38. With respect to the non-linear two-lag model’s specific coefficients, estimates of the advisory’s contemporaneous and second-lag effects on vehicle trips remain statistically insignificant, while the estimate for the first-lag effect remains positive but now marginally insignificant. The first-lag interaction effect \(YellowAdvisory_{t-1}\) \(\times\) \(NotSunday_{t-1}\) remains negative and statistically significant, while the contemporaneous interaction effect \(YellowAdvisory_{t}\) \(\times\) \(Holiday_{t}\) remains positive but marginally insignificant. Results for the non-linear three-lag model are similar. Estimates of the advisory’s contemporaneous and second-lag effects on vehicle trips remain statistically insignificant, while the estimate for the first-lag effect is positive but marginally insignificant. Interestingly, the estimate of the third-lag effect is negative and statistically significant. The first-lag interaction effect \(YellowAdvisory_{t-1}\) \(\times\) \(NotSunday_{t-1}\) remains negative and statistically significant, while the third-lag effect is positive and significant. Lastly, none of the contemporaneous and lagged estimates for the \(YellowAdvisory_{t}\) \(\times\) \(Holiday_{t}\) interaction term are statistically significant.

  39. Results for two- and three-lag models’ coefficients closely mimic those for both the two-lag and three-lag \(YellowAdvisory_t\) models, respectively, with a few exceptions. In the two-lag model, the positive contemporaneous effect of \(YellowAdvisoryPlus1_{t}\) \(\times\) \(Holiday_{t}\) is now statistically significant. In the three-lag model, both the first- and second-lag advisory effects are positive and significant, while the third-lag effect is negative and significant. Both \(YellowAdvisoryPlus1_{t-1}\) x \(NotSunday_{t-1}\) and \(YellowAdvisoryPlus1_{t-2}\) x \(NotSunday_{t-2}\) are negative and significant, and while \(YellowAdvisoryPlus1_{t}\) \(\times\) \(Holiday_{t}\) remains positive and significant, \(YellowAdvisoryPlus1_{t-2}\) \(\times\) \(Holiday_{t-2}\) in now negative and significant.

  40. The Wooldridge (1995) test tolerates heteroskedastic and autocorrelated errors, while Durbin’s and Wu-Hausman’s do not (Baum et al. 2007; Wooldridge 1995).

  41. The coefficient estimates are obtained from a model of the form,

    $$\begin{aligned} \begin{aligned} Advisory_t&= \beta _0 + \beta _1 D.VehicleTrips_t +\beta _2 D.TempDiff_t + \beta _3 D.Humidity_t + \beta _4 D.Wind_t \\&\quad +\beta _5 D.HumWind_t + \beta _6 D.SnowFall_t + \beta _7 D.SnowDepth_t +\mu _t. \end{aligned} \end{aligned}$$

    where again \(Advisory_t\) serves as a placeholder for \(YellowAdvisory_t\) and \(YellowAdvisoryPlus1_t\). Also included as regressors in these respective models (but not shown) are the first lag of \(YellowAdvisory_t\) and first three lags of \(YellowAdvisoryPlus1_t\), which were sufficient to satisfy the null hypotheses of no autocorrelation in the residuals.

  42. We also ran a logistic regression for this model, which assumes that the probability of an advisory being issued is a non-linear combination of the regressors. The results, which are available from the author upon request, were qualitatively similar to those from the linear probability model. This similarity between models was anticipated (c.f., Hellevik 2007; Long 1997). We therefore report the estimates from the linear probability model due to their ease of interpretation.

  43. As we will see below, assuming myopic decision-making among individuals simplifies our model without compromising its relevance to the problem at hand.

  44. Assuming \(\beta ^x_i(\theta _t) \equiv 1-\beta ^z_i(\theta _t)\) is a convenient way to embed the assumption that an increase in \(\beta ^z_i\) in response to an increase in \(\theta _t\) increases the value of an additional unit of \(z_{it}\) relative to \(x_{it}\).

  45. Because individuals are assumed myopic in their decision-making, we could just as well aggregate the individual’s budget constraint over all periods t, i.e., express the constraint instead as \(\sum _tw_{it}=\sum _t\left( p^z_tz_{it}(q_{it})+p^q_tq_{it}+x_{it}\right)\).

  46. Again, we acknowledge that in reality the set of individuals in any given region are likely a convex combination of these three types.

  47. Solving for the relative change in \(q^*_{it}\) is sufficient for the analysis at hand. Deriving the absolute change in \(q^*_{it}\) in response to a change in \(\theta _t\) requires simultaneous differentiation of (A.3) and (A.4).

  48. The corresponding necessary condition for this result is less strict due to the inclusion of the term \(\sum _{j \ne i}\frac{\partial ^2\bar{d}_{jt}}{\partial Q^{***2}_t}\) in the denominator of the expression for \(\partial q^{***}_{it}/\partial \theta _t\) in (A.16), i.e., in \(\Omega _3\).

References

  • Acharya R, Caplan AJ (2020) Optimal investment to control “red air day’’ episodes: lessons from northern Utah, USA. J Environ Econ Policy 9(2):227–250

    Article  Google Scholar 

  • Anderson M (2013) Cache valley to adopt new emission testing program. Retrieved from the internet on 15 November 2013 at http://www.ksl.com/?sid=24395111

  • Andreoni J, Miller J (2002) Giving according to GARP: an experimental test of the consistency of preferences for altruism. Econometrica 70(2):737–753

    Article  Google Scholar 

  • Andreoni J, Rao JM (2011) The power of asking: how communication affects selfishness, empathy, and altruism. J Public Econ 95:513–520

    Article  Google Scholar 

  • Angrist JD, Imbens GW, Rubin DB (1996) Identification of causal effects using instrumental variables. J Am Stat Assoc 91(434):444–455

    Article  Google Scholar 

  • Antweiler W (2015) The economics of altruism. Retrieved from the internet on November 5, 2022 at https://wernerantweiler.ca/blog.php?item=2015-12-24

  • Bamberg S, Fuiji S, Friman M, Grling T (2011) Behaviour theory and soft transport policy measures. Transp Policy 18:228–235

    Article  Google Scholar 

  • Barahona N, Gallego FA, Montero JP (2020) Vintage-specific driving restrictions. Rev Econ Stud 87(4):1646–1682

    Article  Google Scholar 

  • Basmann RL (1960) On finite sample distributions of generalized classical linear identifiability test statistics. J Am Stat Assoc 55(292):650–659

  • Baum CF, Schaffer ME, Stillman S (2007) Enhanced routines for instrumental variables/generalized method of moments estimation and testing. Stata J 7:465–506

    Article  Google Scholar 

  • Bergstrom TC (1999) Systems of benevolent utility functions. J Public Econ Theory 1(1):71–100

    Article  Google Scholar 

  • Bolton G, Ockenfels A (2000) ERC: a theory of equity, reciprocity, and competition. Am Econ Rev 90(1):166–193

    Article  Google Scholar 

  • Bonilla JA (2019) The more stringent, the better? Rationing car use in Bogot\(\acute{a}\) with moderate and drastic restrictions. World Bank Econ Rev 33(2):516–534

    Article  Google Scholar 

  • Burkhardt J, Bayham J, Wilson A, Carter E, Berman JD, O’Dell K, Ford B, Fischer EV, Pierce JR (2019) The effect of pollution on crime: evidence from data on particulate matter and ozone. J Environ Econ Manag 98(C):102267

    Article  Google Scholar 

  • Cannon K (2015) By the numbers: a look at LDS population numbers through the years. Herald Journal, January 22. Retrieved from the internet on June 8, 2021 at https://www.hjnews.com/allaccess/by-the-numbers-a-look-at-lds-population-numbers-through-the-years/article_4c3638b8-a1c8-11e4-bdfd-93284906d52d.html

  • Caplan AJ, Acharya R (2019) Optimal vehicle use in the presence of episodic mobile-source air pollution. Resour Energy Econ 57:185–204

    Article  Google Scholar 

  • Caplan AJ, Kim M-K (2018) A note on mitigating the adverse scale effects associated with daily driving restrictions. Environ Dev Econ 23(1):63–79

    Article  Google Scholar 

  • Census Bureau (2010) American fact finder. Retrieved from the internet on December 17, 2011 at http://factfinder2.census.gov

  • Chen S, Qin P, Tan-Soo J-S, Xu J, Yang J (2020) An econometric approach toward identifying the relationship between vehicular traffic and air quality in Beijing. Land Econ 96(3):333–348

    Article  Google Scholar 

  • Croson R (2007) Theories of commitment, altruism and reciprocity: evidence from linear public goods games. Econ Inq 45(2):199–216

    Article  Google Scholar 

  • Cumby R, Huizinga J (1992) Testing the autocorrelation structure of disturbances in ordinary least squares and instrumental variables regressions. Econometrica 60(1):185–195

    Article  Google Scholar 

  • Cummings R, Walker MB (2000) Measuring the effectiveness of voluntary emission reduction programs. Appl Econ 32(13):1719–1726

    Article  Google Scholar 

  • Cutter WB, Neidell M (2009) Voluntary information programs and environmental regulation: evidence from ‘Spare the Air’. J Environ Econ Manag 58:253–265

    Article  Google Scholar 

  • de Marchi S, Hamilton JT (2006) Assessing the accuracy of self-reported data: an evaluation of the toxics release inventory. J Risk Uncertain 32:57–76

    Article  Google Scholar 

  • Dockery DW, Pope III CA, Xu X, Spengler JD, Ware JH, Fay ME, Ferris BG, Speizer FA (1993) An association between air pollution and mortality in six U.S. cities. N Engl J Med 329(24):1753–1759

    Article  Google Scholar 

  • Durbin J (1954) Errors in variables. Rev Int Stat Inst 22(1/3):23–32

    Article  Google Scholar 

  • Fehr E, Schmidt K (1999) A theory of fairness, competition, and cooperation. Q J Econ 114(3):817–868

    Article  Google Scholar 

  • Fujii S, Bamberg S, Friman M, Grling T (2009) Are effects of travel feedback programs correctly assessed? Transportmetrika 5:43–57

    Article  Google Scholar 

  • Hamilton JT (1995) Pollution as news: media and stock market reactions to the toxic release inventory data. J Environ Econ Manag 28:98–113

    Article  Google Scholar 

  • Hausman JA (1978) Specification tests in econometrics. Econometrica 46(6):1251–1271

    Article  Google Scholar 

  • Hahn RW, Ritz RA (2014) Optimal altruism in public good provision. Economic Studies at Brookings, ES Working Paper Series. Retrieved from the internet on July 8: 2022 at https://doi.org/10.2139/ssrn.2370259

  • Hellevik O (2007) Linear versus logistic regression when the dependent variable is a dichotomy. Qual Quant 43(1):59–74

    Article  Google Scholar 

  • Henry GT, Gordon CS (2003) Driving less for better air: impacts of a public information campaign. J Policy Anal Manag 22(1):45–63

    Article  Google Scholar 

  • Hollenhorst J (2021) Utah air quality alert system gets new color scheme. Deseret News. Retrieved from the internet on June 22, 2021 at https://www.deseret.com/2012/11/26/20510370/

  • Huber PJ (1967) The behavior of maximum likelihood estimates under nonstandard conditions. In: Proceedings of the fifth Berkeley symposium on mathematical statistics and probability, vol 1: Statistics. University of California Press, Berkeley, pp 221–233

  • Kaiser MJ, Edwards-Jones G (2006) The role of ecolabeling in fisheries management and conservation. Conserv Biol 20(2):392–398

    Article  Google Scholar 

  • LSC Transportation Consultants, Inc. (2017) Cache valley short-range transit plan: final report. LSC #164490. Retrieved from the internet on December 16, 2021 at https://cvtdbus.org/wp-content/uploads/2018/09/CVTD-SR-Transit-Plan-Accessible.pdf

  • Lee DS, Lemieux T (2010) Regression discontinuity designs in economics. J Econ Lit 48:281–355

    Article  Google Scholar 

  • Ley E (1997) Optimal provision of public goods with altruistic individuals. Econ Lett 54(1):23–27

    Article  Google Scholar 

  • Ljung GM, Box GEP (1978) On a measure of lack of fit in time series models. Biometrika 65(2):297–303

    Article  Google Scholar 

  • Long JS (1997) Regression models for categorical and limited dependent variables, 1st edn. Sage Publications Inc., Thousand Oaks

    Google Scholar 

  • Moscardini LA, Caplan AJ (2017) Controlling episodic air pollution with a seasonal gas tax: the case of Cache Valley, Utah. Environ Resour Econ 66(4):689–715

    Article  Google Scholar 

  • Moser G, Bamberg S (2008) The effectiveness of soft transport policy measures: a critical assessment and meta-analysis of empirical evidence. J Environ Psychol 28:10–26

    Article  Google Scholar 

  • National Aeronautics and Space Administration (NASA) (2014) Introduction to ozone air pollution. Retrieved from the internet on March 2, 2014 at http://science-edu.larc.nasa.gov/ozonegarden/ozone.php

  • Noonan DS (2011) Smoggy with a chance of altruism: using air quality forecasts to drive behavioral change. Working Paper #2011-08. American Enterprise Institute

  • Ottoni-Wilhelm M, Vesterlund L, Xie H (2017) Why do people give? Testing pure and impure altruism. Am Econ Rev 107(11):3617–3633

    Article  Google Scholar 

  • Perlich P, Hollingshaus M, Harris R, Tennert J, Hogue M (2017) Utah’s longterm demographic and economic projections summary. Research Brief: Kem C. Gardner Policy Institute, Retrieved from the internet on August 7, 2019 at https://gardner.utah.edu/wp-content/uploads/Projections-Brief-Final.pdf

  • Pflueger CE, Wang S (2015) A robust test for weak instruments in Stata. Stata J 15(1):216–225

    Article  Google Scholar 

  • Pope CA III (1989) Respiratory disease associated with community air pollution and a steel mill, Utah Valley. Am J Public Health 79(5):623–628

    Article  Google Scholar 

  • Pope CA III, Thun MJ, Namboodiri MM, Dockery DW, Evans JS, Speizer FE, Heath JCW (1995) Particulate air pollution as a predictor of mortality in a prospective study of U.S. adults. Am J Respir Crit Care Med 151(3pt1):669–674

    Article  Google Scholar 

  • Potter C, Bastounis A, Hartmann-Boyce J, Stewart C, Frie K, Tudor K, Bianchi F, Cartwright E, Cook B, Rayner M, Jebb SA (2021) The effects of environmental sustainability labels on selection, purchase, and consumption of food and drink products: a systematic review. Environ Behav. https://doi.org/10.1177/0013916521995473

    Article  Google Scholar 

  • Ribaudo MO, Horan RD (1999) The role of education in nonpoint source pollution control policy. Rev Agric Econ 21(2):331–343

    Google Scholar 

  • Rihn A, Xuan W, Khachatryan H (2019) Text vs. logo: does eco-label format influence consumers’ visual attention and willingness-to-pay for fruit plants? An experimental auction approach. J Behav Exp Econ 82:101452

    Article  Google Scholar 

  • Rivera N (2021) Air quality warnings and temporary driving bans: evidence from air pollution, car trips, and mass-transit ridership in Santiago. J Environ Econ Manag 108:102454

    Article  Google Scholar 

  • Saberian S, Heyes A, Rivers N (2017) Alerts work! Air quality warnings and cycling. Resour Energy Econ 49:169–189

    Article  Google Scholar 

  • Sargan JD (1958) The estimation of economic relationships using instrumental variables. Econometrica 26:393–415

    Article  Google Scholar 

  • Shumacher I (2010) Ecolabeling, consumers’ preferences, and taxation. Ecol Econ 69:2202–2212

    Article  Google Scholar 

  • Simon HA (1993) Altruism and economics. Am Econ Rev 83(2):156–161

    Google Scholar 

  • Smith VH, Kehoe MR, Cremer ME (1995) The private provision of public goods: altruism and voluntary giving. J Public Econ 58(1):107–126

    Article  Google Scholar 

  • Terry JC, Yandle B (1997) EPA’s toxic release inventory: stimulus and response. Manag Decis Econ 18(6):433–441

    Article  Google Scholar 

  • Tribby CP, Miller HJ, Song Y, Smith KR (2013) Do air quality alerts reduce traffic? An analysis of traffic data from the Salt Lake City metropolitan area, Utah, USA. Transp Policy 30:173–185

  • Utah Climate Center (2016) Climate GISStation(s). Retrieved from the internet on June 23, 2016 at https://climate.usurf.usu.edu/mapGUI/mapGUI.php

  • Utah Department of Environment Quality (UDEQ) (2016a) Particulate matter. Available on the internet at http://www.deq.utah.gov/Pollutants/P/pm/Inversion.htm

  • Utah Department of Environment Quality (UDEQ) (2016b) Information sheet, p 2. Available on the internet at http://www.deq.utah.gov/Topics/FactSheets/docs/handouts/pm25sipfs.pdf

  • Utah Department of Environment Quality (UDEQ) (2016c) Utah air monitoring program. Available on the internet at http://www.airmonitoring.utah.gov/network/Counties.htm

  • Utah Department of Transportation (UDOT) (2014) Traffic statistics. Retrieved from the Internet on April 4, 2014 at http://www.udot.utah.gov/main/f?p=100:pg::::1:T,V:507

  • US Environmental Protection Agency (USEPA) (2016) Particle pollution and your health. Available on the internet at https://www.airnow.gov/index.cfm?action=particle health.index

  • Weather Underground (2016) About our data. Retrieved from the internet on February 2, 2014 at http://www.wunderground.com/about/data.asp

  • Welch E, Gu X, Kramer L (2005) The effects of ozone action day public advisories on train ridership in Chicago. Transp Res Part D Transp Environ 10(6):445–458

    Article  Google Scholar 

  • White H (1980) A heteroskedasticity-consistent covariance matrix estimator and a direct test for heteroskedasticity. Econometrica 48(4):817–838

    Article  Google Scholar 

  • White H (1982) Maximimum likelihood estimation of misspecified models. Econometrica 50(1):1–25

    Article  Google Scholar 

  • Wooldridge JM (1995) Score diagnostics for linear models estimated by two stage least squares. In: Advances in econometrics and quantitative economics: essays in honor of professor C.R. Rao, ed. Maddala GS, Phillips PCB, Srinivasan TN, 66–87. Blackwell Publishing, Oxford

  • Wooldridge JM (2020) Introductory Econometrics: A Modern Approach, 7th Edition. Boston, MA: Cengage Company

  • World Atlas (2021) The busiest rapid transit systems in the US. Retrieved from the internet on June 25, 2021 at https://www.worldatlas.com/articles/the-busiest-rapid-transit-systems-in-the-united-states.html

  • Wu D-M (1973) Alternative tests of independence between stochastic regressors and disturbances. Econometrica 41(4):733–750

    Article  Google Scholar 

  • Zivin JG, Neidell M (2009) Days of haze: environmental information and intertemporal avoidance behavior. J Environ Econ Manag 58(2):119–128

    Article  Google Scholar 

  • Zoe EY (2021) Unwatched pollution: the effect of intermittent monitoring on air quality. Am Econ Rev 111(7):2101–2126

    Article  Google Scholar 

  • Zou EY (2021) Unwatched pollution: the effect of intermittent monitoring on air quality. American Economic Review 111(7):2101–2126

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Funding

This study is funded in part by the Utah Agricultural Experiment Station, UTA0-1646. First-round revisions to the paper were made during the author’s sabbatical leave in 2021–2022, while serving as a U.S. Fulbright Scholar at Ben Gurion University of the Negev, Israel, award 11545-IS. The author thanks Ramjee Acharya for assistance in obtaining the data used in this study, and two anonymous reviewers who helped improve the paper’s final version

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Appendices

Technical Appendix

Mathematical Derivations for the Theoretical Model in Sect. 4

Consider myopic individual (or household) i in a given time period t, who derives benefit from making vehicle trips (e.g., commuting to work, shopping, traveling to recreation sites, etc.), but also incurs costs associated with the aggregate amount of trips taken in i’s community or region during time t (to which individual i contributes atomistically), e.g., in the form of elevated \(PM_{2.5}\) concentrations.Footnote 43 We specify i’s benefit function in period t, \(u_{it}\), as,

$$\begin{aligned} u_{it}=u_{it}\left( z_{it}\left( q_{it}\right) ,x_{it};\beta ^z_i\left( \theta _t\right) ,\beta ^x_i\left( \theta _t\right) \right) , i=1,\ldots ,I, t=1,\ldots ,T, \end{aligned}$$
(A.1)

where \(z_{it}\) represents the amount of a composite good obtained as a function of vehicle usage, denoted as \(q_{it}\), and \(x_{it}\) denotes the composite amount of all other goods not obtained via vehicle usage, i.e., household-produced goods. Information-conditioned parameters \(0<\beta ^z_i(\theta _t)<1\) and \(0<\beta ^x_i(\theta _t)<1\), respectively, parameterize \(z_{it}\) and \(x_{it}\) in function \(u_{it}\) such that \(\beta ^x_i(\theta _t) \equiv 1-\beta ^z_i(\theta _t)\), and \(\theta _t\) is an information parameter representing issuance of a yellow air day advisory when \(PM_{2.5}\) concentrations rise above the 15 \(\upmu /\textrm{m}^3\) threshold.Footnote 44 For ease of exposition and without loss of generality, we assume all variables \(z_{it}\), \(q_{it}\), and \(x_{it}\), and parameters \(\beta ^z_i(\theta _t)\), \(\beta ^x_i(\theta _t)\), and \(\theta _t\) are measured continuously. In particular, increases in \(\theta _t\) imply that the region’s individuals are being supplied with more information (via an advisory) about the onset of a yellow air day.

In addition to standard curvature conditions specified for function \(u_{it}\), i.e., \(\partial u_{it} / \partial z_{it}>0\), \(\partial ^2 u_{it}/\partial z^2_{it}\le 0\), \(\partial u_{it}/\partial x_{it}>0\), \(\partial ^2 u_{it}/\partial x^2_{it}\le 0\), and \(\partial ^2 u_{it}/\partial z_{it}\partial x_{it}=\partial ^2 u_{it}/\partial x_{it}\partial z_{it}> 0\), and for function \(z_{it}\), i.e., \(\partial z_{it}/\partial q_{it}>0\) and \(\partial ^2 z_{it}/\partial q^2_{it}\le 0\), we specify a key curvature condition for the ensuing analysis: \(\partial \beta ^z_{i}/ \partial \theta _t>0\). This condition indicates that, all else equal, the marginal value of \(z_{it}\) (relative to that of \(x_{it}\)) increases with the issuance of a yellow air day advisory, i.e., \(\left( \partial ^2 u_{it}/\partial z_{it}\partial \beta ^z_i\right) \left( \partial \beta ^z_{i}/ \partial \theta _t\right) >0\). Note that identity \(\beta ^x_i(\theta _t) \equiv 1-\beta ^z_i(\theta _t)\) in turn implies \(\left( \partial ^2 u_{it}/\partial x_{it}\partial \beta ^z_i\right) \left( \partial \beta ^z_{i}/ \partial \theta _t\right) <0\). These conditions underlie the intuition expressed in Sect. 4 that, given the issuance of a yellow air day advisory, an individual derives added benefit from any given vehicle trip, since making the trip using the next-best alternative, e.g., walking or riding a bus, involves greater exposure to the yellow air. Furthermore, given that a yellow air day advisory signals the onset of a subsequent red air day episode, individuals could perceive added benefit associated with intertemporally substituting vehicle trips forward in time to reduce the need for making future vehicle trips during the episode itself.

Individual i forms an expectation over the health and environmental damages s/he suffers with respect to aggregate \(PM_{2.5}\) concentrations accumulated in the atmosphere during period t. We represent these expected damages with function \(E\left[ d_{it}\right]\),

$$\begin{aligned} E\left[ d_{it}\right] =\bar{d}_{it}\left( Q_t;\alpha _i\left( \theta _t\right) \right) , i=1,\ldots ,I, t=1,\ldots ,T, \end{aligned}$$
(A.2)

where region-wide vehicle trips \(Q_t=\sum _i q_{it}\), \(\alpha _i\left( \theta _t\right)\) is an information-conditioned parameter distinct from \(\beta ^z_i\), and standard curvature conditions are specified for expected damage function \(E\left[ d_{it}\right]\), i.e., \(\partial \bar{d}_{it}/\partial Q_t >0\), \(\partial ^2 \bar{d}_{it}/\partial Q^2_t \ge 0\), and \(\partial \bar{d}_{it}/\partial \alpha _i >0\). Similar to the relationship between \(\beta ^z_i\) and \(\theta _t\) we assume \(\partial \alpha _{i}/ \partial \theta _t>0\), which in turn indicates that, all else equal, perceived marginal damages suffered by each individual i in period t increase in response to the issuance of a yellow air day advisory, i.e., \(\left( \partial ^2 \bar{d}_{it}/\partial Q_t \partial \alpha _i\right) \left( \partial \alpha _i/\partial \theta _t\right) >0\). This condition accounts for an overall increase in expected marginal damages to an individual’s health due to the issuance of a yellow air day advisory.

The individual’s budget constraint in any given period t is given by,

$$\begin{aligned} w_{it}=p^z_tz_{it}(q_{it})+p^q_tq_{it}+x_{it}, i=1,\ldots ,I, t=1,\ldots ,T, \end{aligned}$$
(A.3)

where \(w_{it}\) represents individual i’s given wealth level in period t, and per-unit prices \(p^z_t\) and \(p^q_t\) are taken as given for good \(z_{it}\) and vehicle trips \(q_{it}\), respectively (the price of \(x_{it}\) is normalized to one).Footnote 45

Next, we consider three cases reflecting three stylized types of individuals comprising the region.Footnote 46 Case 1 pertains to individuals who completely ignore the expected damages associated with region-wide vehicle trips in each period t, \(Q_t\), even though \(\partial \alpha _i/\partial \theta _t \ne 0\), i.e., even though they are informed about elevated \(PM_{2}.5\) concentrations via yellow air day advisories. Case 2 pertains to individuals who account solely for the expected damages that they personally incur in period t, i.e., individual i dissects function \(\bar{d}_{it}\) as \(\bar{d}_{it}\left( q_{it}+Q_{-it};\alpha _i\left( \theta _t\right) \right)\), where \(Q_{-it}\) represents the aggregate trip count across all individuals in the region except individual i, and thereby accounts soley for the \(q_{it}\) in \(\bar{d}_{it}(\cdot )\) in his decision problem. Case 3 pertains to altruistic individuals who account not only for the expected damages that their vehicle trips impose on themselves and all other individuals in the region, but also the expected benefits that all other individuals obtain as a result of increasing their vehicle trips in response to a yellow air day advisory, i.e., these individuals are “pure altruists” (c.f., Antweiler 2015; Ottoni-Wilhelm et al. 2017).

1.1 Case 1

An individual i who fits the description of Case 1 myopically chooses \(q_{it}\) and \(x_{it}\) to solve the following Lagrangian in each period t,

$$\begin{aligned}{} & {} u_{it}\left( z_{it}\left( q_{it}\right) ,x_{it};\beta ^z_i\left( \theta _t\right) ,\beta ^x_i\left( \theta _t\right) \right) -\bar{d}_{it}\left( Q_t;\alpha _i\left( \theta _t\right) \right) \\{} & {} +\lambda _{it}\left( w_{it}-p^z_tz_{it}(q_{it})-p^q_tq_{it}-x_{it}\right) \end{aligned}$$

where \(\lambda _{it}>0\) represents i’s period t Lagrangian multiplier. First-order conditions for this problem result in,

$$\begin{aligned} \frac{\partial u_{it}}{\partial z_{it}}\frac{\partial z_{it}}{\partial q_{it}}=\frac{\partial u_{it}}{\partial x_{it}}\left( p^z_t\frac{\partial z_{it}}{\partial q_{it}}+p^q_t\right) , i=1,\ldots ,I, t=1,\ldots ,T. \end{aligned}$$
(A.4)

The left-hand side of (A.4) represents the marginal benefit of an additional vehicle trip and the right-hand side represents the corresponding marginal cost. Together with (A.3) and function \(z_{it}\left( q_{it}\right)\), Eq. (A.4) solves for \(q^*_{it}=q_{it}\left( w_{it}, p^z_t, p^q_t, \alpha _{i}\left( \theta _t\right) ,\beta ^z_{i}\left( \theta _t\right) ,\beta ^x_{i}\left( \theta _t\right) \right)\), \(z^*_{it}=z_{it}\left( w_{it}, p^z_t, p^q_t, \alpha _{i}\left( \theta _t\right) ,\beta ^z_{i}\left( \theta _t\right) ,\beta ^x_{i}\left( \theta _t\right) \right)\), and \(x^*_{it}=x_{it}\left( w_{it}, p^z_t, p^q_t, \alpha _{i}\left( \theta _t\right) ,\beta ^z_{i}\left( \theta _t\right) , \beta ^x_{i}\left( \theta _t\right) \right)\).

Substituting \(q^*_{it}\), \(z^*_{it}\), and \(x^*_{it}\) into (A.4) and differentiating allows us to solve for the marginal effect of a change in \(\theta _t\) on \(q^*_{it}\) relative to \(x^*_{it}\).Footnote 47 The expression for this marginal effect is,

$$\begin{aligned} \frac{\partial q^*_{it}}{\partial \theta _t}=-\frac{\Psi _1}{\Omega _1}>0, i=1,\ldots ,I, t=1,\ldots ,T, \end{aligned}$$
(A.5)

where

$$\begin{aligned} \Psi _1=\frac{\partial ^2 u_{it}}{\partial z^*_{it}\partial \beta ^z_i}\frac{\partial \beta ^z_i}{\partial \theta _t}\frac{\partial z^*_{it}}{\partial q^*_{it}}-\frac{\partial ^2 u_{it}}{\partial x^*_{it}\partial \beta ^z_i}\frac{\partial \beta ^z_i}{\partial \theta _t}\left( p^z_t\frac{\partial z^*_{it}}{\partial q^*_{it}}+p^q_t\right) >0 \end{aligned}$$
(A.6)

and

$$\begin{aligned} \Omega _1=\frac{\partial ^2 u_{it}}{\partial z^{*2}_{it}}\left( \frac{\partial z^*_{it}}{\partial q^*_{it}}\right) ^2+\frac{\partial u_{it}}{\partial z^{*}_{it}}\frac{\partial ^2 z^*_{it}}{\partial q^{*2}_{it}}-\frac{\partial ^2 u_{it}}{\partial x^*_{it} \partial z^*_{it}}\frac{\partial z^*_{it}}{\partial q^*_{it}}\left( p^z_t\frac{\partial z^*_{it}}{\partial q^*_{it}}+p^q_t\right) -\frac{\partial u_{it}}{\partial x^*_{it}}p^z_t\frac{\partial ^2 u_{it}}{\partial z^{*2}_{it}}<0. \end{aligned}$$
(A.7)

Note that \(\Psi _1>0\) in (A.6) follows directly from the curvature conditions specified above for \(u_{it}\left( \cdot \right)\). To see why \(\Omega _1<0\) in (A.7), first rewrite (A.4) as,

$$\begin{aligned} \frac{\partial u_{it}}{\partial z_{it}}-\frac{\partial u_{it}}{\partial x_{it}}p^z_t=\frac{p^q_t}{\frac{\partial z_{it}}{\partial q_{it}}}>0, i=1,\ldots ,I, t=1,\ldots ,T. \end{aligned}$$
(A.8)

Now note from (A.7) that \(\Omega _1<0\) when

$$\begin{aligned} \left( \frac{\partial u_{it}}{\partial z^{*}_{it}}-\frac{\partial u_{it}}{\partial x^*_{it}}p^z_t\right) \frac{\partial ^2 z^*_{it}}{\partial q^{*2}_{it}}<0 \Longrightarrow \frac{\partial u_{it}}{\partial z^*_{it}}-\frac{\partial u_{it}}{\partial x^*_{it}}p^z_t>0, \end{aligned}$$

which coincides with the result in (A.8). Thus, \(\Omega _1<0\).

Clearly, the result in (A.5) is driven by the assumptions underlying our problem, in particular the separability of \(u_{it}\) and \(\bar{d}_{it}\) in individual i’s Lagrangian function. In a more general specification of i’s welfare, e.g., \(u_{it}\left( z_{it}\left( q_{it}\right) ,x_{it};Q_t,\beta ^z_i\left( \theta _t\right) ,\beta ^x_i\left( \theta _t\right) ,\beta ^Q_i\left( \theta _t\right) \right)\), where \(\beta ^Q_i\left( \theta _t\right) <0\) parameterizes \(Q_t\) in \(u_{it}\), we cannot definitively sign \(\partial q^*_{it}/\partial \theta _t\) without specifying additional assumptions governing the tradeoff between \(z_{it}\) and \(x_{it}\) in response to an increase in \(\theta _t\). As is, our result for Case 1 depicts the predilection of certain types of individuals who weight the private benefit associated with their vehicle trips during yellow air days more than the correlative public damages to which their trips contribute (which, according to our particular welfare specification, are completely ignored in this case).

1.2 Case 2

An individual i who fits the description of Case 2 myopically chooses \(q_{it}\) and \(x_{it}\) to solve the following Lagrangian in each period t,

$$\begin{aligned}{} & {} u_{it}\left( z_{it}\left( q_{it}\right) ,x_{it};\beta ^z_i\left( \theta _t\right) ,\beta ^x_i\left( \theta _t\right) \right) -\bar{d}_{it}\left( q_{it}+Q_{-it};\alpha _i\left( \theta _t\right) \right) \\{} & {} +\gamma _{it}\left( w_{it}-p^z_tz_{it}(q_{it})-p^q_tq_{it}-x_{it}\right) \end{aligned}$$

where \(\gamma _{it}>0\) represents i’s period t Lagrangian multiplier. First-order conditions for this problem result in,

$$\begin{aligned} \frac{\partial u_{it}}{\partial z_{it}}\frac{\partial z_{it}}{\partial q_{it}}=\frac{\partial u_{it}}{\partial x_{it}}\left( p^z_t\frac{\partial z_{it}}{\partial q_{it}}+p^q_t\right) +\frac{\partial \bar{d}_{it}}{\partial Q_t}, i=1,\ldots ,I, t=1,\ldots ,T. \end{aligned}$$
(A.9)

As with Case 1, the left-hand side of (A.9) represents the marginal benefit of an additional vehicle trip and the right-hand side represents the corresponding marginal cost, which in this case now accounts for the individual’s expected marginal damage associated with an additional vehicle trip, \(\partial \bar{d}_{it}/\partial Q_t\). Similar to Case 1, Eq. (A.3), function \(z_{it}\left( q_{it}\right)\), and optimality condition (A.9) solve for \(q^{**}_{it}\), \(z^{**}_{it}\), and \(x^{**}_{it}\), which when substituted back into (A.9) and differentiated allows us to solve for the marginal effect of a change in \(\theta _t\) on \(q^{**}_{it}\) relative to \(x^{**}_{it}\). The expression for this marginal effect is,

$$\begin{aligned} \frac{\partial q^{**}_{it}}{\partial \theta _t}=-\frac{\Psi _2}{\Omega _2}, i=1,\ldots ,I, t=1,\ldots ,T, \end{aligned}$$
(A.10)

where

$$\begin{aligned} \Psi _2=\Psi _1-\frac{\partial ^2\bar{d}_{it}}{\partial Q^{**}_t \partial \alpha _i}\frac{\partial \alpha _i}{\partial \theta _t} \end{aligned}$$
(A.11)

and

$$\begin{aligned} \Omega _2=\Omega _1-\frac{\partial ^2\bar{d}_{it}}{\partial Q^{**2}_t}<0. \end{aligned}$$
(A.12)

Comparing (A.10)–(A.12) with (A.5)–(A.7) we see that,

$$\begin{aligned} \frac{\partial q^{**}_{it}}{\partial \theta _t}<\frac{\partial q^{*}_{it}}{\partial \theta _t}. \end{aligned}$$
(A.13)

Further, we find that,

$$\begin{aligned} \frac{\partial q^{**}_{it}}{\partial \theta _t} \gtrless 0 \, \text {as} \, \frac{\partial ^2\bar{d}_{it}}{\partial Q^{**}_t \partial \alpha _i} \lessgtr \frac{\partial ^2 u_{it}}{\partial z^{**}_{it}\partial \beta ^z_i}\frac{\partial \beta ^z_i}{\partial \theta _t}\frac{\partial z^{**}_{it}}{\partial q^{**}_{it}}-\frac{\partial ^2 u_{it}}{\partial x^{**}_{it}\partial \beta ^z_i}\frac{\partial \beta ^z_i}{\partial \theta _t}\left( p^z_t\frac{\partial z^{**}_{it}}{\partial q^{**}_{it}}+p^q_t\right) , \end{aligned}$$
(A.14)

where the term \(\frac{\partial ^2\bar{d}_{it}}{\partial Q^{**}_t \partial \alpha _i}\) represents the change in individual i’s perceived marginal damage (from vehicle trips) associated with the change in information-conditioned parameter \(\alpha _i\) as a result of the issuance of a yellow air day advisory (i.e., change in \(\theta _t\)). The term \(\frac{\partial ^2 u_{it}}{\partial z^{**}_{it}\partial \beta ^z_i}\frac{\partial \beta ^z_i}{\partial \theta _t}\frac{\partial z^{**}_{it}}{\partial q^{**}_{it}}-\frac{\partial ^2 u_{it}}{\partial x^{**}_{it}\partial \beta ^z_i}\frac{\partial \beta ^z_i}{\partial \theta _t}\left( p^z_t\frac{\partial z^{**}_{it}}{\partial q^{**}_{it}}+p^q_t\right)\) represents the corresponding change in individual i’s marginal benefit associated with the change in information-conditioned parameter \(\beta ^z_i\). Our result for Case 2 therefore depicts a different type of individual than Case 1. In this case, the individual explicitly accounts for the (private effect of) the public damage to which his trips contribute, which leads to a lower increase in vehicle usage in response to a yellow air day advisory than for Case 1 individuals, all else equal. As Eqs. (A.13) and (A.14) demonstrate, Case 2 individuals may choose to decrease the number of their vehicle trips in response to a yellow air day advisory.

1.3 Case 3

An individual i who fits the description of Case 3 myopically chooses \(q_{it}\) and \(x_{it}\) to solve the following Lagrangian in each period t,

$$\begin{aligned}{} & {} u_{it}\left( z_{it}\left( q_{it}\right) ,x_{it}, \sum _{j\ne i}\bar{u}_{jt}\left( z_{jt}\left( q_{jt}\right) ,x_{jt};\beta ^z_j\left( \theta _t\right) ,\beta ^x_j\left( \theta _t\right) \right) ; \beta ^z_i\left( \theta _t\right) ,\beta ^x_i\left( \theta _t\right) \right) \\{} & {} \quad -\bar{d}_{it}\left( q_{it}+Q_{-it};\alpha _i\left( \theta _t\right) \right) \\{} & {} \quad -\sum _{j\ne i}\bar{d}_{jt}\left( q_{it}+Q_{-it};\alpha _j\left( \theta _t\right) \right) \\{} & {} \quad +\phi _{it}\left( w_{it}-p^z_tz_{it}(q_{it})-p^q_tq_{it}-x_{it}\right) \end{aligned}$$

where \(\phi _{it}>0\) represents i’s period t Lagrangian multiplier. An altruistic individual i therefore fully accounts for the effect of a yellow air day advisory on the expected benefits that all other individuals j, \(j \ne i, i,j=1,\ldots ,I\) obtain from their vehicle usage, represented by inclusion of the term \(\sum _{j\ne i}\bar{u}_{jt}\left( z_{jt}\left( q_{jt}\right) ,x_{jt};\beta ^z_j\left( \theta _t\right) ,\beta ^x_j\left( \theta _t\right) \right)\) in i’s own utility function \(u_{it}\). Altruistic individual i also fully accounts for the effects of both the yellow air day advisory and her vehicle usage on the expected damages incurred by all other individuals, represented by inclusion of the separate term \(\sum _{j\ne i}\bar{d}_{jt}\left( q_{it}+Q_{-it};\alpha _j\left( \theta _t\right) \right)\) in her Lagrangian function. First-order conditions for this problem result in,

$$\begin{aligned} \frac{\partial u_{it}}{\partial z_{it}}\frac{\partial z_{it}}{\partial q_{it}}=\frac{\partial u_{it}}{\partial x_{it}}\left( p^z_t\frac{\partial z_{it}}{\partial q_{it}}+p^q_t\right) +\frac{\partial \bar{d}_{it}}{\partial Q_t}+\sum _{j \ne i}\frac{\partial \bar{d}_{jt}}{\partial Q_t}, i,j=1,\ldots ,I, t=1,\ldots ,T. \end{aligned}$$
(A.15)

where \(\partial \bar{d}_{jt}/\partial Q_t>0 \forall j \ne i\), i.e., individual i perceives all other members of the region as suffering positive marginal damages from additional vehicle trips made within the region.

As with Cases 1 and 2, the left-hand side of (A.15) represents the marginal benefit of an additional vehicle trip and the right-hand side represents the corresponding marginal cost, which in this case now accounts for i’s expected private marginal damage associated with taking an additional vehicle trip as well as i’s expectation of the impact that that additional vehicle trip has on the damages incurred by all other individuals in the region, represented by the term \(\sum _{j \ne i}\frac{\partial \bar{d}_{jt}}{\partial Q_t}\). Similar to Cases 1 and 2, Eq. (A.3), function \(z_{it}\left( q_{it}\right)\), and optimality condition (A.15) solve for \(q^{***}_{it}\), \(z^{***}_{it}\), and \(x^{***}_{it}\), which when substituted back into (A.15) and differentiated allows us to solve for the marginal effect of a change in \(\theta _t\) on \(q^{***}_{it}\) relative to \(x^{***}_{it}\). The expression for this marginal effect is,

$$\begin{aligned} \frac{\partial q^{***}_{it}}{\partial \theta _t}=-\frac{\Psi _3}{\Omega _3}, i=1,\ldots ,I, t=1,\ldots ,T, \end{aligned}$$
(A.16)

where

$$\begin{aligned} \Psi _3= & {} \Psi _2+\sum _{j \ne i}\left( \frac{\partial ^2 u_{it}}{\partial z^{***}_{it} \partial \bar{u}_{jt}}\frac{\partial \bar{u}_{jt}}{\partial \beta ^z_j} \frac{\partial \beta ^z_j}{\partial \theta _t}\frac{\partial z^{***}_{it}}{\partial q^{***}_{it}}\right. \nonumber \\{} & {} \left. -\frac{\partial ^2 u_{it}}{\partial x^{***}_{it} \partial \bar{u}_{jt}}\frac{\partial \bar{u}_{jt}}{\partial \beta ^z_j}\frac{\partial \beta ^z_j}{\partial \theta _t}\left( p^z_t \frac{\partial z^{***}_{it}}{\partial q^{***}_{it}}+p^q_t\right) -\frac{\partial ^2\bar{d}_{jt}}{\partial Q^{***}_t \partial \alpha _j}\frac{\partial \alpha _j}{\partial \theta _t}\right) \end{aligned}$$
(A.17)

and

$$\begin{aligned} \Omega _3=\Omega _2-\sum _{j \ne i}\frac{\partial ^2\bar{d}_{jt}}{\partial Q^{***2}_t}<0. \end{aligned}$$
(A.18)

We note that \(\frac{\partial ^2 u_{it}}{\partial z^{***}_{it} \partial \bar{u}_{jt}}>0\) and \(\frac{\partial ^2 u_{it}}{\partial x^{***}_{it} \partial \bar{u}_{jt}}>0\) across all individuals j as a reflection of individual i’s altruism, and \(\frac{\partial \bar{u}_{jt}}{\partial \beta ^z_j}\frac{\partial \beta ^z_j}{\partial \theta _t}\le 0\), which reflects the fact that before any given yellow air day advisory individuals j are assumed to have optimally set their respective \(\beta ^z_j\left( \theta _t \right)\) parameter values.

Comparing (A.10)–(A.12) with (A.16)–(A.18) leads to a sufficient condition governing the relationship between \(\partial q^{***}_{it}/\partial \theta _t\) and \(\partial q^{**}_{it}/\partial \theta _t\) across all \(i,j=1,\ldots ,I\), and \(t=1,\ldots ,T\),Footnote 48

$$\begin{aligned} \frac{\partial q^{***}_{it}}{\partial \theta _t}< & {} \frac{\partial q^{**}_{it}}{\partial \theta _t} \quad \text {if} \quad \sum _{j \ne i}\left( \frac{\partial ^2 \bar{d}_{jt}}{\partial Q^{***}_t \partial \alpha _j} \frac{\partial \alpha _j}{\partial \theta _t}\right) >\nonumber \\&\quad&\sum _{j \ne i}\left( \frac{\partial ^2 u_{it}}{\partial z^{***}_{it} \partial \bar{u}_{jt}}\frac{\partial \bar{u}_{jt}}{\partial \beta ^z_j}\frac{\partial \beta ^z_j}{\partial \theta _t}\frac{\partial z^{***}_{it}}{\partial q^{***}_{it}}\right) \nonumber \\{} & {} \quad -\sum _{j \ne i}\left( \frac{\partial ^2 u_{it}}{\partial x^{***}_{it} \partial \bar{u}_{jt}}\frac{\partial \bar{u}_{jt}}{\partial \beta ^z_j}\frac{\partial \beta ^z_j}{\partial \theta _t}\left( p^z_t \frac{\partial z^{***}_{it}}{\partial q^{***}_{it}}+p^q_t\right) \right) . \end{aligned}$$
(A.19)

The left-hand side of the second inequality in (A.19) represents the change in individual i’s perceived marginal damage associated with the added aggregate damage suffered by individuals \(j \ne i\) (from their vehicle trips) brought about by the respective changes in their information-conditioned parameters \(\alpha _j\) as a result of the issuance of a yellow air day advisory (i.e., change in \(\theta _t\)). The right-hand side of the second inequality represents the corresponding change in i’s perceived marginal benefit associated with the added aggregate benefit obtained by individuals \(j \ne i\) brought about by the respective changes in their information-conditioned parameters \(\beta ^z_j\).

Similarly, comparing (A.5)–(A.7) with (A.16)–(A.18) leads to a sufficient condition governing the relationship between \(\partial q^{***}_{it}/\partial \theta _t\) and \(\partial q^{*}_{it}/\partial \theta _t\) across all \(i,j=1,\ldots ,I\), and \(t=1,\ldots ,T\),

$$\begin{aligned} \frac{\partial q^{***}_{it}}{\partial \theta _t}< & {} \frac{\partial q^{*}_{it}}{\partial \theta _t} \quad \text {if} \quad \frac{\partial ^2 \bar{d}_{it}}{\partial Q^{***}_t \partial \alpha _i}\frac{\partial \alpha _j}{\partial \theta _t} +\sum _{j \ne i}\left( \frac{\partial ^2 \bar{d}_{jt}}{\partial Q^{***}_t \partial \alpha _j} \frac{\partial \alpha _j}{\partial \theta _t}\right) >\nonumber \\{} & {} \sum _{j \ne i}\left( \frac{\partial ^2 u_{it}}{\partial z^{***}_{it} \partial \bar{u}_{jt}}\frac{\partial \bar{u}_{jt}}{\partial \beta ^z_j}\frac{\partial \beta ^z_j}{\partial \theta _t}\frac{\partial z^{***}_{it}}{\partial q^{***}_{it}}\right) \nonumber \\{} & {} -\sum _{j \ne i}\left( \frac{\partial ^2 u_{it}}{\partial x^{***}_{it} \partial \bar{u}_{jt}}\frac{\partial \bar{u}_{jt}}{\partial \beta ^z_j}\frac{\partial \beta ^z_j}{\partial \theta _t}\left( p^z_t \frac{\partial z^{***}_{it}}{\partial q^{***}_{it}}+p^q_t\right) \right) , \end{aligned}$$
(A.20)

where the left-hand and right-hand sides of the second inequality in (A.20) have the same interpretations as those in the second inequality in Eq. (A.19). However, in this case the sufficient condition is now more likely to hold because of the addition of the \(\frac{\partial ^2 \bar{d}_{it}}{\partial Q^{***}_t \partial \alpha _i}\frac{\partial \alpha _j}{\partial \theta _t}>0\) term on the left-hand side of the second inequality.

Coefficient Plots for the Empirical Analysis in Sect. 6.2

Fig. 6
figure 6

Coefficient plots for \(YellowAdvisoryPlus1_t\)

Fig. 7
figure 7

Coefficient plots for \(YellowAdvisory_{t-1}\)

Fig. 8
figure 8

Coefficient plots for \(YellowAdvisoryPlus1_{t-1}\)

Fig. 9
figure 9

Source https://onlinelibrary.utah.gov/utah/counties/ and https://www.freeworldmaps.net/united-states/utah/location.html

Location of Cache Valley, Utah

Model 1 includes only contemporaneous effects associated with \(YellowAdvisory_t\).

Model 2 includes both contemporaneous and single-day lag effects associated with \(YellowAdvisory_t\).

Model 3 adds a second-day lag effect to Model 2.

Model 4 is the quadratic model with two-day lag effects.

Model 5 is the quadratic model with three-day lag effects.

Model 1 includes only contemporaneous effects associated with \(YellowAdvisoryPlus1_t\).

Model 2 includes both contemporaneous and single-day lag effects associated with \(YellowAdvisoryPlus1_t\).

Model 3 adds a second-day lag effect to Model 2.

Model 4 is the quadratic model with two-day lag effects.

Model 5 is the quadratic model with three-day lag effects.

Model 1 includes only single-day lag effects associated with \(YellowAdvisory_{t-1}\).

Model 2 includes both contemporaneous and single-day lag effects associated with \(YellowAdvisory_t\).

Model 3 adds a second-day lag effect to Model 2.

Model 4 is the quadratic model with two-day lag effects.

Model 5 is the quadratic model with three-day lag effects.

Model 1 includes only single-day lag effects associated with \(YellowAdvisoryPlus1_{t-1}\).

Model 2 includes both contemporaneous and single-day lag effects associated with \(YellowAdvisoryPlus1_t\).

Model 3 adds a second-day lag effect to Model 2.

Model 4 is the quadratic model with two-day lag effects.

Model 5 is the quadratic model with three-day lag effects.

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Caplan, A.J. Missing the Warning Signs? The Case of “Yellow Air Day” Advisories in Northern Utah. Environ Resource Econ 85, 479–522 (2023). https://doi.org/10.1007/s10640-023-00773-7

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