Next Article in Journal
Sustainable Municipal Energy Transition—Evaluating Support and Citizens’ Awareness Levels in the Post-Mining Region in Poland
Previous Article in Journal
Signal or Noise? Readability and Signaling in the First Year of IFRS S2 Sustainability Reporting in an Emerging Market: Evidence from Türkiye
Previous Article in Special Issue
Advancing Inclusive, Multimodal, Climate-Resilient Planning for Rural Networked Transport Infrastructure
 
 
Font Type:
Arial Georgia Verdana
Font Size:
Aa Aa Aa
Line Spacing:
Column Width:
Background:
Article

Probabilistic Modeling of Inter-Vehicle Spacing on Two-Lane Roads: Implications for Safety-Oriented and Sustainable Traffic Operations

by
Andrea Pompigna
1,*,
Giuseppe Cantisani
2 and
Giulia Del Serrone
2
1
Faculty of Technological & Innovation Sciences, Universitas Mercatorum, Piazza Mattei 10, 00186 Rome, Italy
2
Department of Civil, Constructional and Environmental Engineering, University of Rome La Sapienza, Via Eudossiana 18, 00184 Rome, Italy
*
Author to whom correspondence should be addressed.
Sustainability 2026, 18(6), 2896; https://doi.org/10.3390/su18062896
Submission received: 16 February 2026 / Revised: 8 March 2026 / Accepted: 12 March 2026 / Published: 16 March 2026

Abstract

Accurate characterization of inter-vehicle spacing is fundamental for safety assessment and sustainable operation of road networks, particularly on two-lane rural roads where monitoring infrastructure is limited. Unlike temporal headways, vehicle spacing directly reflects physical vehicle interactions and roadway occupancy, making it a more appropriate variable for evaluating collision risk and operational efficiency. This study develops a probabilistic framework for modeling vehicle spacing based on the statistical isomorphism between Event Flows and Linear Fields of Random Points. Using a calibrated microscopic simulation model, spacing distributions are generated for unidirectional traffic over flow rates from 100 to 1300 veh/h. A Pearson Type III distribution is shown to consistently reproduce the observed asymmetry, kurtosis, and non-zero minimum spacing across traffic regimes. Distribution parameters are estimated via maximum likelihood and validated using a heuristic Kolmogorov–Smirnov procedure suitable for large samples. Results demonstrate systematic relationships between spacing distribution parameters and macroscopic traffic variables, enabling estimation of the probability of unsafe spacing conditions from commonly available traffic data. The proposed framework supports sustainability-oriented traffic management by providing a quantitative basis for safety evaluation and operational control without requiring extensive sensing infrastructure.

1. Introduction

Rear-end collisions and inefficient utilization of roadway capacity remain central challenges for sustainable traffic systems, particularly on two-lane rural roads where geometric constraints and limited instrumentation restrict technological interventions. At the microscopic level, both safety and operational performance are governed by inter-vehicle spacing, which directly reflects physical vehicle interactions and roadway occupancy. Consequently, spatial spacing represents a primary variable for sustainability-oriented traffic analysis, as it influences collision risk, traffic organization, and infrastructure efficiency.
Vehicle spacing, also referred to as distance headway or spatial headway, is defined as the longitudinal distance between two successive vehicles measured at a given instant along a roadway segment, typically between homologous reference points on consecutive vehicles. Conversely, vehicle headway, or temporal headway, represents the time interval between successive vehicles passing the same point on the same lane at a fixed cross section. Although both variables describe microscopic traffic interactions, spatial spacing directly reflects the physical occupation of road space and the organization of traffic streams, whereas temporal headways provide only indirect information mediated by vehicle speed.
Vehicle spacing is a fundamental element of traffic analysis due to its direct relationship with vehicle density and its influence on driving behavior, safety conditions, and infrastructure performance [1,2]. Through this relationship, spacing affects traffic characteristics and levels of service on uninterrupted-flow facilities, such as multilane highways and freeways [1,3,4].
Historically, research on vehicle interactions has concentrated primarily on temporal headways. As reviewed by [5], early headway studies from the 1930s to the 1970s [6,7,8,9,10] and later developments addressing higher traffic demands on increasingly crowded roads [11,12,13] focused on vehicle arrival processes observed at fixed cross sections. These approaches implicitly assumed that headway distributions measured at a point were representative of vehicle interactions along an entire roadway segment. Subsequent studies demonstrated that headway distributions vary with traffic state, speed, and interaction intensity and therefore cannot be considered spatially homogeneous [5,14,15,16].
Although temporal headways are easier to collect using fixed-point detectors, they provide only indirect information on physical vehicle proximity and implicitly assume homogeneous speeds. Under real traffic conditions, speed variability introduces additional randomness that breaks the equivalence between time-based and space-based observations. As a result, temporal headways cannot reliably represent actual inter-vehicle separation along a road segment. In contrast, spatial spacing directly quantifies physical distance between vehicles and is therefore more appropriate for evaluating collision risk, roadway occupancy, and compliance with safety thresholds.
Proper understanding of vehicle spacing is essential for developing traffic models that enhance safety, support sustainability objectives, establish safe following distances, and inform regulatory standards. Rear-end collisions, which account for a substantial portion of traffic accidents, often result from sudden deceleration of the leading vehicle or unexpected acceleration of the following vehicle, primarily due to driver inattention, misjudgment, or aggressive [17,18,19,20]. Consequently, analyzing vehicle behavior in terms of spatial distancing is fundamental for modeling rear-end collision mechanisms and testing mitigation strategies.
Direct measurement of spatial spacing over extended road segments poses practical challenges, particularly on rural networks. While speeds and temporal headways are easily collected using fixed-point detectors, spatial spacing is often inferred indirectly through local density estimates based on stationarity assumptions that are rarely satisfied under real traffic conditions [1,2,21]. Experimental approaches using GPS, LiDAR, or instrumented vehicles provide accurate spacing measurements but are typically limited in scale and applicability [22]. Recent advances in video recording and image processing enable high-resolution spacing measurements [17,23], yet these technologies require substantial infrastructure and are generally confined to motorways and major corridors [24]. In recent years, UAV-based aerial video combined with computer-vision trajectory reconstruction has enabled the collection of high-resolution microscopic traffic data, including vehicle trajectories and spatial gaps, over extended road segments [25,26,27]. However, such approaches typically require dedicated survey campaigns, regulatory authorization, and significant data-processing resources, and their systematic deployment over extended rural networks remains operationally constrained.
Two-lane rural roads represent a substantial share of national and regional road networks and play a key role in connecting urban areas with local and peripheral territories. These facilities are characterized by heterogeneous traffic, geometric constraints, and limited technological equipment [28,29,30]. From a sustainability standpoint, improving safety and operational efficiency on such roads is essential, as extensive infrastructure upgrades or sensor deployments are often economically and environmentally unfeasible. In this context, modeling approaches capable of extracting meaningful information from commonly available traffic data are particularly valuable.
Probabilistic modeling provides a suitable framework for representing inter-vehicle spacing under these constraints. Empirical evidence shows that spacing distributions are asymmetric, bounded, and strongly dependent on traffic conditions, reflecting the coexistence of free-flow and interaction-dominated regimes [9,10,11]. Despite their relevance, spatial spacing distributions have received less attention than temporal headways, particularly for two-lane rural roads, where their characterization can support sustainable traffic management and safety-oriented decision making.
The present study addresses this gap by focusing on the probabilistic characterization of inter-vehicle spacing on no-passing two-lane rural roads. To overcome the lack of direct spacing measurements, the research adopts the isomorphism between Event Flows and Linear Fields of Random Points [21], which provides a theoretical basis for deriving spacing distributions from temporal headway distributions. Building on the simulation model proposed by [31], calibrated and validated using monitored data from a two-lane rural road section in Northern Italy, this study analyzes spacing distributions across a wide range of traffic flow rates and densities.
The objective is to identify and estimate an appropriate probabilistic representation of vehicle spacing, focusing on the Pearson Type III distribution, and to investigate the behavior of its parameters as traffic conditions evolve. The Pearson Type III family is selected because it provides a flexible three-parameter formulation capable of simultaneously representing positive skewness, leptokurtic behavior, and non-zero minimum spacing values, while encompassing classical models such as the Negative Exponential, Shifted Exponential, and Erlang distributions as special cases. This property allows a unified distributional framework across different traffic regimes without switching between unrelated functional forms. By providing a statistically consistent description of spacing, the proposed framework supports sustainability-oriented traffic analysis by enabling quantitative safety assessment, performance evaluation, and regulatory considerations without requiring extensive monitoring infrastructure.
The principal scientific contribution of this study is the formulation and validation of a probabilistic framework for inter-vehicle spacing on two-lane rural roads, based on the isomorphism between Event Flows and Linear Fields of Random Points and implemented through the Pearson Type III distribution, whose parameters exhibit systematic relationships with macroscopic traffic variables.
The remainder of the paper is organized as follows. Section 2 presents the problem formulation and introduces the theoretical framework based on Event Flows and Linear Fields isomorphism. Section 3 summarizes the simulation model and the spacing datasets used in the analysis. Section 4 presents the estimation of spacing probability distributions using the Pearson Type III family. Section 5 discusses parameter trends across traffic conditions. Finally, Section 6 summarizes the main conclusions.

2. Theoretical Framework: Point Processes and Vehicle Spacing

This section outlines the stochastic framework used to connect temporal headways (measured at a cross section) and spatial spacings (measured along a road segment) using point-process theory. The framework provides the basis for selecting and calibrating probabilistic models for inter-vehicle spacing under different traffic regimes.

2.1. Traffic Counting Process and Vehicle Headway Process

Microscopic traffic behavior emerges from heterogeneous driver–vehicle units that continuously adjust their motion in response to the leading vehicle. As a result, both temporal headways and spatial spacings exhibit substantial variability, even when roadway conditions are uniform and demand is approximately stable. When traffic is treated as a stochastic process, a practical and comprehensive description is obtained by specifying the probability density function of inter-event (time) or inter-object (space) separations together with information on serial dependence (e.g., autocorrelation) [10,21].
Even under stationary traffic conditions, inter-vehicle separation exhibits inherent variability due to heterogeneity in vehicle performance and driver perception–reaction behavior. Consequently, sequences of headways or spacings can be modeled as realizations of a random process, which is central to both theoretical and applied traffic-flow analysis [21].
A random process can be viewed as a finite-length series of measurements of a random variable over an observation horizon T [1,21]. In this context, a traffic lane can be conceptualized as a family of stochastic trajectories [10]: the n-th vehicle is represented by its position x n t over time t, and the collection { x n t } forms a mutually dependent family of functions. An observer at a fixed roadside location x = x a records vehicle passage times t 0 , t 1 , t 2 , … and the temporal headways ( t 1 t 0 ) , ( t 2 t 1 ) , … become the primary objects of interest rather than the absolute passage instants. Within this “local” observation setting, the headway probability density function is fundamental, because it supports derivation of the counting distribution, i.e., the probability distribution of the number of vehicles arriving in a fixed observation interval–an essential element for assessing temporal dependence in traffic phenomena [10,21].
An alternative boundary condition is defined by observing the traffic stream at a fixed time t = t b . In that “instantaneous” setting, the relevant quantities are spatial spacings ( x i x i 1 ) , which again carry greater significance than absolute vehicle positions. Instantaneous observations support estimation of spatial speeds and densities, whereas local observations yield time-mean speeds and volumes. In line with most of the literature, the present study primarily uses the local view to describe inter-event intervals (temporal headways) and then exploits the corresponding isomorphic structure to infer spatial spacing behavior.

2.2. Linear Point Processes

Separations between consecutive vehicles (in time or space) are more informative than absolute locations and the relationship between temporal-headway distributions and spatial-spacing distributions can be formalized through point-process theory, specifically via Event Flows and Linear Fields of Objects [32,33].
A point process is a stochastic model for points (events or objects) randomly located in a mathematical space (time, a line, a plane, or higher-dimensional spaces). In one dimension, point processes describe random occurrence of events/objects in time or along a line [33,34]. Randomness is a defining feature of point processes, but independence is not: independence holds only for specific models (e.g., Poisson), whereas more general processes incorporate interaction effects (repulsion/attraction) that change the distribution of inter-point distances.
Consider the positive half-line r + . A linear random point process is defined as a progressive random placement of points on r + , represented by increasing random abscissas x 1 , x 2 , …, x n (Figure 1).
The inter-point distances are Δ i x = x i + 1 x i with i = 1,2, …, n and the process can equivalently be described by the sequence x 1 ; x 2 = x 1 + Δ 1 x ; x 3 = x 1 + Δ 1 x + Δ 2 x and so forth. The average number β of points per unit interval on r + is the process intensity, which may be constant, β = cost, or variable, β = β x .
The same mathematical structure admits different physical interpretations. If points represent events and the abscissas represent event times t i (i.e., x i = t i ), the process is an Event Flow, also known as an Arrival Process, with interarrival times τ i = t = t i + 1 t i and λ is the event rate (e.g., traffic flow rate). If points represent objects aligned along a line and the abscissas represent positions along r + , the process is a Linear Field of Objects with interspaces s i = Δ i l = l i + 1 l i , and β is the object density. In traffic terms, Event Flows represent vehicle passages at a cross section, whereas Linear Fields represent vehicle positions along a road segment at an instant.

2.2.1. Isomorphism Between Event Flows and Linear Fields for Time and Space Headways

Event Flows and Linear Fields of Objects arise from the same ordered random-point construction on r + and are therefore statistically isomorphic in a formal sense. The isomorphism establishes a duality between time and space, and correspondingly between flow rate and density, provided that the same probabilistic assumptions apply. Importantly, this is an equivalence between stochastic model structures, not an automatic physical identity between time-based and space-based measurements.
Consider a vehicle arrival process that satisfies the following [30]:
  • Absence of memory: counts in disjoint time intervals are independent;
  • Ordinariness: probability of two or more arrivals in a short interval is negligible relative to a single arrival;
  • Stationarity: arrival intensity γ is constant over time.
Then, the number of arrivals m in a time interval Δt follows a Poisson law:
P m = a m m ! e a
where m = 0 , 1,2 , , n , and
a = γ Δ t
Under Equation (1), inter-arrival times are exponentially distributed:
f τ = γ · e x p γ τ
Replacing events with objects and Δ t with a special segment Δ l on r + yields a Poisson Linear Field of Objects with analogous assumptions:
  • Absence of memory: counts in disjoint segments are independent;
  • Ordinariness: probability of two or more objects in a short segment is negligible;
  • Stationarity: density γ is constant along r + .
The number of objects in a segment Δ l still follows Equation (1) with a = γ Δ l , and the interspaces are exponential:
f s = γ · e x p γ s
In traffic terms, if Equation (3) models temporal headways at a cross section with γ = Q (flow rate), Equation (4) models spatial spacings along a segment with γ = D   (density). Thus, for Poisson Event Flows and Poisson Linear Fields, the same functional form (negative exponential) applies to both temporal and spatial separations when expressed in the corresponding domain.
More generally, for any pair of statistically isomorphic Event Flow and Linear Field models, the spatial-distance law has the same functional form as the temporal law under the dual substitutions   Q   D and t   l . This establishes the conceptual duality: flow rate and time are dual to density and length. However, empirical coincidence between time-headway and space-spacing distributions requires homogeneous traffic with constant and identical speeds. When speeds vary, transforming time into space introduces additional randomness, and temporal and spatial distributions generally differ even if the underlying model structures remain isomorphic.

2.2.2. Some Models for the Spatial Distance Between Vehicles

The isomorphism provides a principled way to derive candidate spacing models from temporal-headway models for steady-state single-lane traffic. Common temporal-headway models include the Negative Exponential, Shifted Exponential, Erlang, and Lognormal distributions [1,11,21]. For low-density traffic without platoons, the Negative Exponential model represents maximal randomness in arrivals and has CDF:
F τ = 1 γ · e x p γ τ
where γ denotes the intensity of the underlying Poisson Event Flow.
Because Equation (5) assigns non-zero probability to arbitrarily small headways, it conflicts with finite vehicle length. A standard remedy is the Shifted Exponential model incorporating a minimum feasible headway τ 0 [5,10,35]:
F τ = 1 e x p τ τ 0 1 γ τ 0 , τ τ 0
where the normalization preserves mean 1 / γ .
When interactions increase and headways concentrate into narrower ranges, Erlang or Log-normal models are often appropriate [35,36,37,38,39]:
F τ = 1 e x p τ k γ n = 0 k 1 τ k γ n n !
F τ = Φ l n τ α β
where Φ(∙) is the standard normal CDF.
Table 1 reports the corresponding spacing models obtained by substituting τs and QD [21]. For Negative Exponential and Shifted Exponential spacing distributions, γ = D. In the Erlang case, the rate becomes k D , where k ∈ {1, 2, …} controls shape; s 0 is the minimum feasible spacing; α and β are the mean and variance of ln(s). Sample statistics s ¯ and S 2 ¯ estimate μ s = E s and σ 2 s = V A R s .
From an application standpoint, a Negative Exponential spacing model is consistent with sparse, non-platooned streams. The Shifted Exponential accommodates a minimum distance s 0 . As density increases and vehicle interactions become stronger, an Erlang distribution can provide a better representation. The Log-normal can be suitable in dense regimes where spacings concentrate into a small number of amplitude classes.
The Erlang distribution can also be interpreted as the inter-arrival distribution between non-consecutive events (e.g., the nth and (n + k)th) in a Palm Event Flow [40] which generalizes Poisson flow by allowing limited dependence while maintaining stationarity. This structure makes Erlang models useful when interdependence is present but does not extend to long memory [41]. Empirical fitting of Erlang models under different discharge regimes is documented in prior works [1,42,43,44].
As an initial model-selection heuristic, moment-based criteria can be used: if s ¯ S 2 ¯ , a Negative Exponential model is plausible (Table 1). A Shifted Exponential may be adopted when a non-zero minimum distance is required. When s ¯ S 2 ¯ , spacing variability departs from that implied by a Poisson Linear Field, and alternative models such as Erlang become appropriate.

2.2.3. Pearson Type III Distribution and Spatial Distances Between Vehicles

Several headway/spacing models that appear distinct (excluding Log-normal) can be embedded within a unified distributional family, increasing modeling flexibility without switching between unrelated functional forms. This is achieved through the Pearson Type III distribution, a three-parameter member of the Pearson distribution family.
Pearson Type III has a long tradition in hydrology and has been extensively studied for parameter estimation and fitting procedures [45,46,47]. Buckley [10] first proposed its use in traffic, showing good fit for non-low flow conditions [9].
Hereafter, β denotes the point-process intensity (i.e., γ = Q for Event Flows and γ = D   for Linear Fields). To avoid ambiguity, the Pearson Type III distribution is parameterized by shape k , location s 0 , and rate λ = 1 / θ .
For spacing s, Pearson Type III (three-parameter gamma/shifted gamma) is defined for s s 0 by:
f s = λ Γ k · λ s s 0 k 1 e x p λ s s 0 ,   s s 0 ,
or equivalently, with λ = 1 θ ,
f s = s s 0 k 1 θ k Γ k · e x p s s 0 θ ,   s s 0 .
The Gamma function is
Γ k = 0 x k 1 e x d x ,
so that for integer k , Γ k = k 1 ! .
Parameters have clear roles: k > 0 controls shape/skewness, s 0 R is a location (minimum spacing) parameter, and λ 0 (or θ > 0) controls scale. For spacing applications, λ > 0 and s ∈ ( s 0 , + ).
Pearson Type III subsumes several classical models as special cases: for s 0 = 0 and real k > 1 , it yields the Gamma distribution; for s 0 = 0 and integer k , it yields Erlang; for s 0 = 0 , k = 1 , it reduces to Negative Exponential; for s 0 > 0 , k = 1 , it yields Shifted Exponential (Table 1). In the Poisson (exponential) special case k = 1 , s 0 = 0 , the Pearson rate coincides with the Linear Field intensity, i.e., λ = γ = D ; for k 1 and/or s 0 > 0 , λ is a distributional parameter linked to, but not directly interpretable as, traffic density.
The mean and variance are μ = s 0 + k λ , σ 2 = k λ 2 , and skewness equals to 2 k , decreasing as k increases. Parameters k , λ = 1 θ , and s 0 can be estimated by the method of moments [48], or via maximum likelihood estimation (MLE). For a sample s 1 ,   s 2 ,   ,   s n with s 0 < m i n i s i , the likelihood is:
L k ,   θ , s 0 = i = 1 n s i s 0 k 1 θ k Γ k · e x p s i s 0 θ   s 0 < m i n i s i
The log-likelihood is:
l o g L k ,   θ , s 0 = i = 1 n k 1 · l n s i s 0 s i s 0 θ k · l n θ l n Γ k ,   s i s 0 > 0
Pearson Type III can model asymmetric data beyond classical event-flow assumptions. Unlike its Erlang specialization, it does not explicitly embed the limited-memory structure associated with Palm event flows or modified Poisson processes [49]. More generally, it does not require independence or limited memory in its theoretical construction [50]. Nonetheless, assessing dependence remains important to avoid biased inference and misinterpretation of statistical tests [51]. For sequential spacing/headway data, dependence can be screened through lag-1 autocorrelation: a significant lag-1 correlation indicates that each observation depends partly on its predecessor [52]. While such dependence does not invalidate Pearson Type III as a descriptive distribution, it may affect standard inference procedures and motivates robustness checks and appropriate estimation strategies [53].
Building on the probabilistic framework introduced in Section 2, the following section describes the simulation-based methodology adopted to generate and analyze inter-vehicle spacing data under controlled traffic conditions.

3. Methods and Materials

3.1. Spacing Simulation Model for a Single-Lane Traffic Stream

This study develops a probabilistic characterization of inter-vehicle spacing that can support safety-oriented and sustainable traffic operations on two-lane rural roads, where extensive sensing infrastructure is often impractical. Building on the theoretical isomorphism between Event Flows and Linear Fields of Random Points on the semi-infinite line r + , the paper focuses on selecting and calibrating a probability model for spacing under operating conditions that enforce single-lane behavior (i.e., no overtaking). The spacing datasets analyzed herein are generated using the calibrated Spacing Simulation Model introduced in [31]. The complete modeling chain, including model assumptions, calibration procedures, and validation results, is presented in detail in the previous study [28], which provides the empirical basis for the simulation framework adopted here.
The simulation framework consists of two main components: a Vehicle-Generation Model (VGM) and a Vehicle-Interaction Model (VIM).
The VGM defines vehicle entry at the origin O of a lane of indefinite length and includes:
  • Temporal Headway Distribution Model (THDM): assigns a stochastic temporal headway to each vehicle relative to its predecessor;
  • Initial Speed Distribution Model (ISDM): assigns entry speeds at O using a stochastic representation consistent with the macroscopic fundamental diagram, thereby capturing realistic variability in driver behavior and vehicle performance.
The VIM governs longitudinal interactions after entry and includes:
  • First Vehicle Speed Pattern (FVSP): prescribes the motion pattern of the lead vehicle;
  • Car-Following Model (CFM): reproduces the response of each following vehicle in terms of speed and spacing adaptation to the leader, incorporating reaction effects and collision-avoidance constraints.
In the adopted framework, vehicle interactions are modeled through General Motors (GM) car-following formulation. The parameters α 0 , m , and l are defined consistently with the macroscopic traffic law calibrated for the monitored site. In particular, the values m = 0 and l = 1 associate the GM formulation with the Greenberg fundamental diagram calibrated for the reference road section, while the sensitivity parameter α 0 is set equal to the characteristic speed parameter V m of the same diagram, as reported [31]. This ensures consistency between the microscopic interaction mechanism and the macroscopic traffic relationships observed in the field.
Vehicles are represented as extended objects with constant length L = 4.5   m, consistent with the passenger-car length observed at the monitoring site. This value corresponds to the average vehicle length measured in the calibrated dataset and reflects the single-class traffic composition of the study site, where heavy vehicles over 3.5 tons are not permitted.
Simulations cover hourly flow rates from 100 to 1300 veh/h in increments of 100 veh/h. For each flow level, 100 independent sequences of 100 vehicles are generated (single vehicle class, no overtaking). Vehicles enter at O according to THDM and ISDM and then interact according to the CFM under FVSP, producing a controlled yet behaviorally consistent stream suitable for systematic spacing analysis.
Model specification, calibration, and validation rely on the monitoring section described in [29]. The site consists of a straight, level two-lane rural road segment in Northern Italy instrumented with 24.165 GHz Doppler radar sensors on both sides. The facility has a 90 km/h speed limit, a no-transit rule for heavy vehicles over 3.5 tons, and a no-overtaking rule for all vehicle categories. Traffic was monitored over 24 h in both directions, capturing approximately 28,000 vehicles during a typical workday without atmospheric or incidental disruptions. The monitoring data collected at this site were used in [31] to calibrate the parameters of the vehicle-generation process, the stochastic fundamental diagram, and the GM car-following model, and to validate the simulated traffic variables (speeds and headways) against observed measurements.
Overall, 130,000 vehicles are simulated (13 flow levels × 100 sequences × 100 vehicles). For each 100-vehicle sequence, the following variables are extracted:
  • Temporal headways τ i ( x = 0 ) ( i = 1 , , 100 ) at the origin O;
  • Speeds V i ( x = 0 ) ( i = 1 , , 100 ) at the origin O;
  • Spacing s i ( t = t * ) ( i = 1 , , 100 ), at the reference time t * , defined as the longitudinal separation between vehicle i and its predecessor at the instant when the last vehicle ( i = 100 ) enters the stream, thus providing an instantaneous spatial snapshot of the traffic configuration.
As reported in [31], simulated headways and entry speeds were validated against the monitored data, showing strong agreement both for headway distributions and for speed trends consistent with the macroscopic behavior observed at the site. This validation supports the use of the simulated spacing datasets for the probabilistic analyses developed in the present paper.

3.2. Spacing Data Simulated at Varying Flow Rates and Densities

The analyses focus on spacing observations s i ( t = t * ) ( i = 1 , , 100 ) collected at the reference time t * , i.e., when the last vehicle of each 100-vehicle sequence is generated at the origin O. In the simulation output, spacing is defined as the longitudinal distance between homologous reference points on consecutive vehicles (front-to-front in the simulated representation) and therefore includes the vehicle length   L . Accordingly, the gross spacing can be written as s i g t * = Δ x i t * . A net physical gap can be obtained by subtracting vehicle length :   s i n ( t * ) = Δ x i ( t * ) L , with L = 4.5 m.
In the following, only the gross spacing s i g ( t * ) is considered because it ensures that spacing measurements refer to a consistent homologous point on successive vehicles and remains fully coherent with the point-based probabilistic framework and the extended-vehicle representation adopted in the simulation model. For simplicity, the notation s i ( t * ) is used to denote gross spacing unless otherwise stated.
Spacing data are analyzed to characterize the probabilistic behavior of inter-vehicle separation under varying traffic conditions. The study considers flow classes from 100 to 1300 veh/h (step 100 veh/h) and density classes from 1 to 45 veh/km (step 5 veh/km). The simulated flow is normalized to an hourly rate using transits between t = 0 and t = t * , while density is computed at t *   by normalizing the number of simulated vehicles to a 1 km road segment based on the total inter-point spacing along the road axis.
Further details and descriptive statistics of spacing for each class (central tendency, dispersion, quartiles, skewness, and kurtosis) can be found in [31]. The key empirical characteristics motivating the distributional modeling in this paper are summarized as follows:
  • Positive skewness: spacing distributions are right-skewed, with most values concentrated at low spacings and occasional large separations;
  • High kurtosis: distributions are leptokurtic, indicating a pronounced peak and heavier tails than a normal distribution;
  • Non-zero minimum values: minimum spacings reflect kinematic constraints and interaction rules embedded in the simulation;
  • Autocorrelation at high traffic levels: dependence becomes more evident at higher flow and density regimes.
Consistent with these features and with the evidence reported in [31], the Pearson Type III distribution provides a flexible parametric representation capable of reproducing asymmetry, kurtosis, and non-zero minima. Moreover, unlike exponential or Erlang-based formulations, Pearson Type III does not require independence or limited-memory assumptions and can therefore be applied to datasets exhibiting interdependencies, as supported by the lag-1 autocorrelation analyses in [31]. These datasets constitute the empirical basis for the parameter estimation and goodness-of-fit analyses presented in Section 4.

4. Results

To quantify and model spacing dynamics, the parameters of the Pearson Type III distribution are estimated separately for classes of hourly traffic volume and for classes of traffic density, each defined by a specific range of vehicles per hour or per kilometer.
Thus, for the set of 1300 simulated series, each consisting of 100 vehicles generated by the simulation, two fitting analyses of the Pearson Type III distribution were carried out, for: simulated flow segmentation ( Q ranging from 100 to 1300 vehicles/hour with an increment of 100 vehicles/hour); and simulated density segmentation ( D ranging from 1 to 45 vehicles/km with an increment of 5 vehicles/km). For the estimation of the parameters k and λ in Equation (9), the MATLAB 2020a function ‘gamfit’ was used, which is based on the MLE method. This was preceded by a data shift equal to the estimated location parameter s 0 , to reduce the three-parameter Pearson Type III distribution to a standard Gamma form suitable for MLE.
As is well-known in the practice of data fitting, an assessment of autocorrelation is crucial for understanding its potential impact on parameter estimation. As highlighted in [31], the analysis can be confined to autocorrelation at lag 1, assuming no compelling reasons exist for higher lag autocorrelations among vehicle distances unless a correlation at lag 1 (i.e., among three consecutive vehicles) is present. Based on the results in [31], it can be stated that, generally, in situations of low traffic volume where autocorrelation is less pronounced, the estimation of parameters is statistically reliable. However, at higher traffic volumes, even though the focus is placed on the average values of the estimated parameters, verifying that increased autocorrelation does not significantly distort the results involves evaluating the consistency of parameter trends with varying traffic volume and density. If the parameters vary predictably and without anomalies across different traffic classes, it can be concluded that the effect of autocorrelation, while present, does not compromise the validity of the Gamma distribution parameter estimates. In this context, MLE is used to estimate the parameters of the marginal spacing distribution rather than to perform statistical inference based on asymptotic standard errors. The objective of the analysis is the identification of the appropriate probabilistic form and the examination of the evolution of the distribution parameters across traffic regimes. Consequently, the robustness of the estimation under serial dependence is assessed through the regularity and coherence of the parameter trends with respect to traffic flow and density. Any possible underestimation of variance due to autocorrelation therefore mainly affects the quantification of parameter uncertainty, while it does not alter the identification of the distributional form describing inter-vehicle spacing.
For each class of Q and D , Table 2 and Table 3 show the values of the estimated parameters. The same tables report the goodness-of-fit (GoF) test, which is performed with the heuristic criterion defined in [30] to address the oversensitivity of traditional tests when dealing with large datasets. Thus, a heuristic Kolmogorov–Smirnov (KS) goodness-of-fit procedure was considered as a practical GoF assessment under large-sample conditions, through resampling a large number (1000) of small random sub-samples (100) compared to the hundreds of thousands of headways in the original samples.
The proposed criterion for assessing the overall GoF involves calculating the KS D n statistic (namely the maximum difference between the theoretical and observed cumulated frequencies) for each sub-sample and obtaining their average D n ¯ . By comparing the mean value D n ¯ with the critical value, it provides a basis for accepting or rejecting the null hypothesis for the entire dataset. With a significance level of α = 0.05 , the critical value of the KS test is K S C α = 0.05 , n = 100 = 0.136 .
Table 2 and Table 3 present the mean value D n ¯ of the D n statistic over 1000 random sub-samples of size 100. It also indicates (**) if the null hypothesis that the empirical distribution is consistent with the estimated theoretical distribution is not rejected based on the heuristic criterion D n ¯ < K S C α = 0.05 , n = 100 and on the mean of the relative p-value values of each D n (which must be >0.05).
Table 2 and Table 3 also contain the expected value of spacing calculated based on the distribution parameters as E s = s 0 + k / λ and the average density E D = 1000 / ( k / λ + s 0 ) (veh/km) always calculated using the parameters of the estimated probability distribution function.
It can be observed that, for all flow rate classes reported in Table 2, the null hypothesis that the empirical spacing distribution is consistent with the Pearson Type III distribution with the estimated parameters is not rejected. A similar result is obtained for the density classes reported in Table 3, with one exception corresponding to the lowest density class (1–5 veh/km). In this case, although the mean p-value remains above the prescribed significance threshold, the mean KS statistic D n ¯ is very close to the critical value.
This behavior can be attributed to the higher heterogeneity of traffic conditions characterizing this density range, which includes simulated flow rates between 100 and 400 veh/h and average speeds ranging from approximately 90.5 to 63.5 km/h. To account for this heterogeneity, Table 4 reports the results of the parameter estimation, goodness-of-fit assessment, expected spacing E [ s ] , and estimated density E D for simulated densities between 1 and 5 veh/km, disaggregated with a step of 1 veh/km. The five disaggregated density classes all exhibit D n ¯ values below the critical threshold and substantially lower than those obtained for the aggregated class, indicating a marked improvement in goodness-of-fit.
The corresponding probability density functions of the Pearson Type III distribution, parameterized according to Table 2, Table 3 and Table 4, are illustrated in Figure 2a, Figure 2b and Figure 2c, respectively.

5. Discussion

The analysis of vehicle spacings using the Pearson Type III distribution has proven effective in capturing the main statistical features of the simulated traffic data. The estimated parameters provide meaningful insight into traffic dynamics and inter-vehicle interactions under varying operating conditions. Overall, the flexibility of the Pearson Type III distribution allows it to accommodate both the asymmetry and the leptokurtic nature of spacing distributions observed across different flow and density regimes.
In this section, the trends of the estimated distribution parameters and selected characteristic quantities are discussed with respect to hourly traffic flow and vehicle density. Figure 3, Figure 4 and Figure 5 illustrate the variation in the parameters λ and k across the different traffic classes considered.
Consistent with expected driving behavior, the rate parameter λ increases with increasing traffic flow and density. This trend reflects a progressive reduction in average inter-vehicle spacing as traffic conditions become more congested. From a mathematical perspective, higher values of λ correspond to a stronger concentration of probability mass at lower spacing values, since the parameter governs the rate at which the distribution decays. As a result, larger values of λ   indicate more compact vehicle configurations along the road axis.
A comparison between Figure 3a, Figure 4a and Figure 5a highlights different functional relationships between λ and the macroscopic traffic variables. For the flow rate classes, the variation of λ is well approximated by a power-law relationship, indicating an accelerating increase in the parameter as flow rises. In particular, Figure 3a suggests the presence of two distinct regimes separated by a threshold around 600 veh/h: a regime of moderate parameter growth at lower flows and a regime of more rapid growth beyond this value. This threshold is consistent with the calibrated fundamental diagrams for the same road section, which indicate that around Q 600 veh/h traffic transitions from weak interaction conditions to a regime dominated by car-following. As vehicle interactions become systematic and platoons form, spacing becomes more constrained, explaining the faster growth of λ beyond this flow level. In contrast, when λ is analyzed as a function of traffic density, Figure 4a and Figure 5a show a nearly linear trend, both for density classes with a step of 5 veh/km and for the finer disaggregation below 5 veh/km.
The shape parameter k plays a critical role in determining the form of the Pearson Type III distribution and the degree of variability around the mean spacing. For k < 1 , the distribution is highly skewed with a mode at zero, indicating pronounced variability and a high frequency of very small spacings. When k = 1 , the distribution reduces to the exponential case, corresponding to maximum randomness. For k > 1 , the mode shifts away from zero and the distribution becomes progressively more symmetric, with reduced relative variability. As shown in Figure 3b and Figure 5b, the estimated values of k range approximately between 0.7 and 1.3, reflecting higher variability at low flow and low density levels and a tendency toward stabilization as traffic density increases.
The relationships illustrated in Figure 3, Figure 4 and Figure 5 describe the evolution of the estimated distribution parameters as functions of traffic flow and density. These relationships provide an interpretable and analytically tractable representation of spacing dynamics and can be directly employed in safety-oriented assessments and evaluations of compliance with regulatory spacing requirements, as further discussed in this section.
Figure 6, Figure 7 and Figure 8 further illustrate characteristic trends of the estimated Pearson Type III distributions across the different flow rate and density classes. Specifically, Figure 6a, Figure 7a and Figure 8a show the variation of the expected spacing value associated with each estimated distribution, which, according to the model parameters, is given by E [ s ] = s 0 + k / λ . In all cases, the observed trend of the expected spacing is accurately represented by a negative power-law function, highlighting the systematic reduction in average spacing as traffic conditions become more congested.
Additional insight is provided by Figure 6b, Figure 7b and Figure 8b, which depict the expected average density derived from the estimated spacing distributions, defined as E D = 1000 / ( k / λ + s 0 ) .  Figure 6b shows a close correspondence between the density values E D inferred from the estimated spacing distributions (vertical axis) and the trend predicted by the Greenberg macroscopic model (horizontal axis), thereby providing further support for the adequacy of the fitted probability distributions. A similar confirmation is provided by Figure 7b and Figure 8b, where the expected average density is compared with the mean density of each class, yielding a linear correlation coefficient very close to unity.

6. Conclusions

This study emphasizes the central role of inter-vehicle spacing, interpreted as spatial headway, for the microscopic analysis of traffic streams on two-lane rural roads operating under unidirectional, single-lane conditions. Although temporal headways have been extensively investigated in the literature, they describe vehicle arrivals at a fixed point and provide only indirect information on physical proximity between vehicles. In contrast, spatial spacing directly represents instantaneous vehicle configurations along the roadway and therefore constitutes a more appropriate variable for assessing collision risk, roadway occupancy, and operational efficiency. Despite this relevance, spacing distributions have received comparatively limited attention. This paper contributes to addressing this gap by developing a probabilistic framework for modeling vehicle spacings under varying traffic volumes and densities.
The principal scientific contribution of this study is the formulation and validation of a probabilistic model for inter-vehicle spacing on two-lane rural roads, based on a flexible parametric distribution and characterized by systematic relationships between distribution parameters and macroscopic traffic variables.
The theoretical foundation of the study is based on the statistical isomorphism between Event Flows and Linear Fields of Random Points, which establishes a formal correspondence between temporal and spatial processes. This framework enables derivation of spacing probability laws from point-process theory while recognizing that, under real traffic conditions with speed variability, temporal and spatial distributions are generally not physically equivalent. Building on this theoretical structure, the calibrated simulation methodology introduced in [31] was employed to generate spacing datasets across a wide range of traffic regimes. These datasets provided the empirical basis for estimating and validating spacing probability distributions, which were consistently and accurately represented by the Pearson Type III family. The Pearson Type III distribution was selected because it provides a three-parameter formulation capable of representing positive skewness, non-zero minimum spacing, and regime-dependent dispersion within a single functional form, while encompassing classical models such as the Negative Exponential, Shifted Exponential, and Erlang distributions as special cases, thereby ensuring a unified representation of spacing across traffic conditions.
The results show that Pearson Type III distributions capture the essential statistical properties of inter-vehicle spacing, including pronounced positive skewness, leptokurtic behavior, non-zero minimum spacing imposed by kinematic and interaction constraints, and increasing autocorrelation under higher flow and density conditions. Importantly, the estimated distribution parameters exhibit systematic and interpretable trends with respect to both hourly traffic flow and vehicle density. The consistency between densities inferred from the fitted spacing distributions and those implied by macroscopic traffic relationships confirms that the proposed probabilistic formulation preserves fundamental traffic dynamics rather than acting as a purely statistical approximation.
From an applied perspective, these findings provide a practical pathway for linking microscopic vehicle interactions with macroscopic traffic variables. By relating spacing distributions to commonly available measurements such as flow and density, the proposed framework enables estimation of the probability of unsafe following conditions without requiring continuous vehicle-position tracking. This capability is particularly relevant for rural road networks, where dense sensing infrastructure is often economically and environmentally impractical. In this context, probabilistic spacing models offer an effective tool for identifying critical operating regimes, supporting compliance with spacing-related safety standards, and informing traffic management strategies aimed at improving both safety and operational sustainability.
The methodology also establishes a statistical foundation for applications in advanced driver assistance systems, collision warning algorithms, and vehicle-to-vehicle communication strategies, where knowledge of the probabilistic structure of inter-vehicle spacing is essential for defining adaptive safety thresholds. In this sense, the contribution to sustainability arises not only through improved safety outcomes but also through enhanced traffic efficiency and reduced dependence on costly monitoring technologies.
Some limitations should be acknowledged. The analysis focuses on unidirectional traffic on two-lane rural roads under no-overtaking conditions and assumes a homogeneous vehicle class with constant length. In addition, the spatial spacing distributions are derived from a calibrated microscopic simulation model and are not yet cross-validated against independent, directly monitored spatial gap datasets (e.g., UAV-based or trajectory-reconstructed measurements). Moreover, although autocorrelation effects are examined and shown not to compromise parameter estimation, the framework remains distribution-based and does not explicitly model the full temporal dependence structure of vehicle interactions.
Future research will extend the present results by using calibrated spacing distributions to derive safety-oriented indicators explicitly linked to minimum following-distance criteria and rear-end collision exposure across traffic regimes. A priority research step will consist in acquiring and analyzing directly observed spatial vehicle spacing data along two-lane rural road segments in order to perform independent empirical validation of the proposed probabilistic model. This development will provide an operational connection between probabilistic spacing models, regulatory compliance, and longitudinal safety, advancing toward a unified framework for assessing safety, efficiency, and sustainability on two-lane road systems.

Author Contributions

Conceptualization, A.P., G.C. and G.D.S.; methodology, A.P. and G.D.S.; software, A.P.; validation, G.D.S.; formal analysis, A.P. and G.D.S.; investigation, A.P. and G.D.S.; data curation, A.P. and G.D.S.; writing—original draft preparation, A.P.; writing—review and editing, G.D.S.; supervision, G.C.; project administration, G.C. All authors have read and agreed to the published version of the manuscript.

Funding

This research received no external funding.

Institutional Review Board Statement

Not applicable.

Informed Consent Statement

Not applicable.

Data Availability Statement

The raw data from simulation supporting the conclusions of this article will be made available by the authors on request.

Conflicts of Interest

The authors declare no conflicts of interest.

References

  1. Guerrieri, M.; Mauro, R. A Concise Introduction to Traffic Engineering; Springer: Berlin, Germany, 2021. [Google Scholar]
  2. Ni, D. Traffic Flow Theory: Characteristics, Experimental Methods, and Numerical Techniques; Butterworth–Heinemann: Oxford, UK, 2015. [Google Scholar]
  3. Transportation Research Board; National Research Council. Highway Capacity Manual; Transportation Research Board: Washington, DC, USA; National Research Council: Washington, DC, USA, 2022. [Google Scholar]
  4. Mannering, F.L.; Washburn, S.S. Principles of Highway Engineering and Traffic Analysis; John Wiley & Sons: Hoboken, NJ, USA, 2020. [Google Scholar]
  5. Li, L.; Chen, X.M. Vehicle headway modeling and its inferences in macroscopic/microscopic traffic flow theory: A survey. Transp. Res. Part C Emerg. Technol. 2017, 76, 170–188. [Google Scholar] [CrossRef]
  6. Adams, W.F. Road Traffic Considered as a Random Series. Oper. Res. Q. 1950, 1, 9. [Google Scholar]
  7. Gerlough, D.L.; Schuhl, A. Use of Poisson distribution in highway traffic. In The Probability Theory Applied to Distribution of Vehicles on Two-Lane Highways; Eno Foundation for Highway Traffic Control, Inc.: Washington, DC, USA, 1955. [Google Scholar]
  8. Dawson, R.F.; Chimini, L.A. The Hyperlang Probability Distribution: A Generalized Traffic Headway Model; University of Connecticut, School of Engineering, Civil Engineering Department: Storrs, CT, USA, 1967. [Google Scholar]
  9. Buckley, D.J. A semi-Poisson model of traffic flow. Transp. Sci. 1968, 2, 107–133. [Google Scholar] [CrossRef]
  10. Buckley, D.J. Inter-Vehicle Spacing and Counting Distributions. Ph.D. Thesis, University of New South Wales, Sydney, Australia, 1965. [Google Scholar]
  11. Cowan, R.J. Useful headway models. Transp. Res. 1975, 9, 371–375. [Google Scholar] [CrossRef]
  12. Luttinen, R.T. Statistical Properties of Vehicle Time Headway. Ph.D. Thesis, Helsinki University of Technology, Espoo, Finland, 1996. [Google Scholar]
  13. Luttinen, R.T. Properties of Cowan’s M3 headway distribution. Transp. Res. Rec. 1999, 1678, 189–196. [Google Scholar] [CrossRef]
  14. Hoogendoorn, S.P.; Bovy, P.H.L. State-of-the-art of vehicular traffic flow modelling. Proc. Inst. Mech. Eng. Part I J. Syst. Control. Eng. 2001, 215, 283–303. [Google Scholar] [CrossRef]
  15. Jabari, S.E.; Zheng, J.; Liu, H.X. A probabilistic stationary speed–density relation based on Newell’s simplified car-following model. Transp. Res. Part B Methodol. 2014, 68, 205–223. [Google Scholar] [CrossRef]
  16. Zou, Y.; Zhang, Y.; Zhu, X. Constructing a bivariate distribution for freeway speed and headway data. Transp. A Transp. Sci. 2014, 10, 255–272. [Google Scholar] [CrossRef]
  17. Luo, Q.; Zang, X.; Yuan, J.; Chen, X.; Yang, J.; Wu, S. Research of vehicle rear-end collision model considering multiple factors. Math. Probl. Eng. 2020, 2020, 6725408. [Google Scholar] [CrossRef]
  18. Chae, C.; Kim, Y. Investigation of following vehicles’ driving patterns using spectral analysis techniques. Sustainability 2023, 15, 10539. [Google Scholar] [CrossRef]
  19. National Highway Traffic Safety Administration (NHTSA). Traffic Safety Facts: 2019 Data; U.S. Department of Transportation: Washington, DC, USA, 2020.
  20. Tak, S.; Kim, S.; Lee, D.; Yeo, H. A comparison analysis of surrogate safety measures with car-following perspectives for advanced driver assistance systems. J. Adv. Transp. 2018, 2018, 8040815. [Google Scholar] [CrossRef]
  21. Mauro, R. Traffic and Random Processes; Springer: Cham, Switzerland, 2015. [Google Scholar]
  22. Yu, R.; Zhang, Y.; Wang, L.; Du, X. Time headway distribution analysis of naturalistic road users based on aerial datasets. J. Intell. Connect. Veh. 2022, 5, 149–156. [Google Scholar] [CrossRef]
  23. Zhang, Y.; Jia, R.-S.; Yang, R.; Sun, H.M. DSNet: A vehicle density estimation network based on multi-scale sensing of vehicle density in video images. Expert Syst. Appl. 2023, 234, 121020. [Google Scholar] [CrossRef]
  24. Elsagheer Mohamed, S.A.; Alshalfan, K.A.; Al-Hagery, M.A.; Ben Othman, M.T. Safe Driving Distance and Speed for Collision Avoidance in Connected Vehicles. Sensors 2022, 22, 7051. [Google Scholar] [CrossRef] [PubMed]
  25. Krajewski, R.; Bock, J.; Kloeker, L.; Eckstein, L. The highD dataset: A drone dataset of naturalistic vehicle trajectories on German highways for validation of highly automated driving systems. In Proceedings of the 21st International Conference on Intelligent Transportation Systems (ITSC); IEEE: Maui, HI, USA, 2018; pp. 2118–2125. [Google Scholar]
  26. Berghaus, M.; Lamberty, S.; Ehlers, J.; Kalló, E.; Oeser, M. Vehicle trajectory dataset from drone videos including off-ramp and congested traffic—Analysis of data quality, traffic flow, and accident risk. Commun. Transp. Res. 2024, 4, 100133. [Google Scholar]
  27. Chaudhari, A.A.; Treiber, M.; Okhrin, O. MiTra: A drone-based trajectory dataset for an all-traffic-state inclusive freeway with ramps. Sci. Data 2025, 12, 1174. [Google Scholar]
  28. Al-Kaisy, A. Two-lane highways: Indispensable rural mobility. Encyclopedia 2022, 2, 625–631. [Google Scholar] [CrossRef]
  29. Mauro, R.; Pompigna, A. A Statistically Based Model for the Characterization of Vehicle Interactions and Vehicle Platoons Formation on Two-Lane Roads. Sustainability 2022, 14, 4714. [Google Scholar] [CrossRef]
  30. Cantisani, G.; Del Serrone, G.; Mauro, R.; Peluso, P.; Pompigna, A. Traffic stream analysis by radar sensors on two-lane roads for free-moving and constrained vehicles identification. Sensors 2023, 23, 6922. [Google Scholar] [CrossRef] [PubMed]
  31. Pompigna, A.; Cantisani, G.; Mauro, R.; Del Serrone, G. Modeling intervehicle spacing for safe and sustainable operations on two-lane roads. Sustainability 2025, 17, 3602. [Google Scholar] [CrossRef]
  32. Stoyan, D.; Penttinen, A. Recent applications of point process methods in forestry statistics. Stat. Sci. 2000, 15, 61–78. [Google Scholar] [CrossRef]
  33. Daley, D.J.; Vere-Jones, D. An Introduction to the Theory of Point Processes, Volume II: General Theory and Structure; Springer: New York, NY, USA, 2003. [Google Scholar]
  34. Møller, J.; Waagepetersen, R.P. Statistical Inference and Simulation for Spatial Point Processes; Chapman & Hall/CRC: Boca Raton, FL, USA, 2004. [Google Scholar]
  35. Branston, D. Models of single-lane time headway distributions. Transp. Sci. 1976, 10, 125–148. [Google Scholar]
  36. Helbing, D. Fundamentals of traffic flow. Phys. Rev. E 1997, 55, 3735–3738. [Google Scholar] [CrossRef]
  37. Gazis, D.C.; Herman, R.; Rothery, R.W. Nonlinear follow-the-leader models of traffic flow. Oper. Res. 1961, 9, 545–567. [Google Scholar]
  38. Herman, R.; Montroll, E.W.; Potts, R.B.; Rothery, R.W. Traffic dynamics: Analysis of stability in car-following. Oper. Res. 1959, 7, 86–106. [Google Scholar] [CrossRef]
  39. Herman, R.; Rothery, R.W. Microscopic and macroscopic aspects of single-lane traffic flow. Oper. Res. Jpn. 1962, 7, 74–90. [Google Scholar]
  40. Cox, D.R.; Smith, W.L. Queues; Methuen: London, UK, 1961. [Google Scholar]
  41. Baccelli, F.; Brémaud, P. Elements of Queueing Theory: Palm Martingale Calculus and Stochastic Recurrences; Springer: Berlin, Germany, 2003. [Google Scholar]
  42. Ben-Edigbe, J.; Rahman, R.; Mashros, N. Headway distributions based on empirical Erlang and Pearson Type III time methods compared. Res. J. Appl. Sci. Eng. Technol. 2014, 7, 4410–4414. [Google Scholar]
  43. Mauro, R.; Branco, F.; Guerrieri, M. Contribution to the platoon distribution analysis in steady-state traffic conditions. Period. Polytech. Civ. Eng. 2014, 58, 217–227. [Google Scholar] [CrossRef][Green Version]
  44. Mauro, R.; Branco, F. Two vehicular headways time dichotomic models. Mod. Appl. Sci. 2012, 6, 12. [Google Scholar] [CrossRef]
  45. Shaligram, V.M.; Lele, V.S. Analysis of hydrologic data using Pearson Type III distribution. Hydrol. Res. 1978, 9, 31–42. [Google Scholar] [CrossRef]
  46. Singh, V.P. Pearson Type III distribution. In Entropy-Based Parameter Estimation in Hydrology; Springer: Dordrecht, The Netherlands, 1998; Volume 30. [Google Scholar]
  47. Koutrouvelis, I.A.; Canavos, G.C. Estimation in the Pearson Type III distribution. Water Resour. Res. 1999, 35, 2693–2704. [Google Scholar] [CrossRef]
  48. Buckett, J.; Oliver, F.R. Fitting the Pearson Type III distribution in practice. Water Resour. Res. 1977, 13, 851. [Google Scholar] [CrossRef]
  49. Johnson, N.L.; Kotz, S.; Balakrishnan, N. Continuous Univariate Distributions; John Wiley & Sons: Hoboken, NJ, USA, 1994. [Google Scholar]
  50. Klugman, S.A.; Panjer, H.H.; Willmot, G.E. Loss Models: From Data to Decisions; Wiley: Hoboken, NJ, USA, 2012. [Google Scholar]
  51. Davison, A.C. Statistical Models; Cambridge University Press: Cambridge, UK, 2003. [Google Scholar]
  52. Box, G.E.P.; Jenkins, G.M.; Reinsel, G.C. Time Series Analysis: Forecasting and Control; John Wiley & Sons: Hoboken, NJ, USA, 2015. [Google Scholar]
  53. Cox, D.R.; Hinkley, D.V. Theoretical Statistics; Chapman & Hall: London, UK, 1974. [Google Scholar]
Figure 1. Linear random point process on the positive half-line r + .
Figure 1. Linear random point process on the positive half-line r + .
Sustainability 18 02896 g001
Figure 2. Estimated Pearson Type III of spacings: (a) PDFs for groupings of simulated flow rate (bins of 100 veh/h); (b) PDFs for groupings of simulated density (bins of 5 veh/km); (c) PDFs for groupings of simulated density (bins of 1 veh/km between 1 and 5 veh/km).
Figure 2. Estimated Pearson Type III of spacings: (a) PDFs for groupings of simulated flow rate (bins of 100 veh/h); (b) PDFs for groupings of simulated density (bins of 5 veh/km); (c) PDFs for groupings of simulated density (bins of 1 veh/km between 1 and 5 veh/km).
Sustainability 18 02896 g002aSustainability 18 02896 g002b
Figure 3. Estimated parameters for Pearson Type III PDFs for groupings of simulated flow rate (bins of 100 veh/h) (dots: empirical data; dashed line: fitted equation): (a) parameter λ ; (b) parameter k .
Figure 3. Estimated parameters for Pearson Type III PDFs for groupings of simulated flow rate (bins of 100 veh/h) (dots: empirical data; dashed line: fitted equation): (a) parameter λ ; (b) parameter k .
Sustainability 18 02896 g003
Figure 4. Estimated parameters for Pearson Type III PDFs for groupings of simulated density (bins of 5 veh/km) (dots: empirical data; dashed line: fitted equation): (a) parameter λ ; (b) parameter k .
Figure 4. Estimated parameters for Pearson Type III PDFs for groupings of simulated density (bins of 5 veh/km) (dots: empirical data; dashed line: fitted equation): (a) parameter λ ; (b) parameter k .
Sustainability 18 02896 g004
Figure 5. Estimated parameters for Pearson Type III PDFs for groupings of simulated density (bins of 1 veh/km between 1 and 5 veh/km) (dots: empirical data; dashed line: fitted equation): (a) parameter λ ; (b) parameter k .
Figure 5. Estimated parameters for Pearson Type III PDFs for groupings of simulated density (bins of 1 veh/km between 1 and 5 veh/km) (dots: empirical data; dashed line: fitted equation): (a) parameter λ ; (b) parameter k .
Sustainability 18 02896 g005
Figure 6. Estimated Pearson Type III PDFs for groupings of simulated flow rate (bins of 100 veh/h) (dots: empirical data; dashed line: fitted equation): (a) Expected value of spacing distribution E[s] = s 0 + k / λ ; (b) E D = 1000 / ( k / λ + s 0 ) .
Figure 6. Estimated Pearson Type III PDFs for groupings of simulated flow rate (bins of 100 veh/h) (dots: empirical data; dashed line: fitted equation): (a) Expected value of spacing distribution E[s] = s 0 + k / λ ; (b) E D = 1000 / ( k / λ + s 0 ) .
Sustainability 18 02896 g006
Figure 7. Estimated Pearson Type III PDFs for groupings of simulated density (bins of 5 veh/km) (dots: empirical data; dashed line: fitted equation): (a) Exp. value of spacing distribution E[s] = s 0 + k / λ ; (b) E D = 1000 / ( k / λ + s 0 ) vs. simulated density.
Figure 7. Estimated Pearson Type III PDFs for groupings of simulated density (bins of 5 veh/km) (dots: empirical data; dashed line: fitted equation): (a) Exp. value of spacing distribution E[s] = s 0 + k / λ ; (b) E D = 1000 / ( k / λ + s 0 ) vs. simulated density.
Sustainability 18 02896 g007
Figure 8. Estimated Pearson Type III PDFs for groupings of simulated density (bins of 1 veh/km between 1 and 5 veh/km) (dots: empirical data; dashed line: fitted equation): (a) Exp. value of spacing distribution E[s] = s 0 + k / λ ; (b) E D = 1000 / ( k / λ + s 0 ) vs. simulated density.
Figure 8. Estimated Pearson Type III PDFs for groupings of simulated density (bins of 1 veh/km between 1 and 5 veh/km) (dots: empirical data; dashed line: fitted equation): (a) Exp. value of spacing distribution E[s] = s 0 + k / λ ; (b) E D = 1000 / ( k / λ + s 0 ) vs. simulated density.
Sustainability 18 02896 g008
Table 1. Theoretical distributions of the distances s: probability density function (pdf); moments; parameter estimation.
Table 1. Theoretical distributions of the distances s: probability density function (pdf); moments; parameter estimation.
DistributionNeg. ExponentialShifted ExponentialErlangLognormal
pdf γ · e x p γ s 0 for   s < s 0 1 1 γ s 0 · e x p 1 γ s 0 s s 0 for   s s 0 γ · e x p γ s γ s k 1 k 1 ! 1 s β 2 π e x p ln s α 2 2 β 2
Mean   μ 1 γ 1 γ + s 0 k γ e x p α + β 2 2
Variance   σ 2 1 γ 2 1 γ 2 k γ 2 e x p 2 α + β 2 e x p β 2 1
Parameters estimation/model selection 1 γ = s ¯
1 γ 2 = S 2 ¯
s 0 = s ¯ S 2 ¯
1 γ 2 = S 2 ¯
γ = s ¯ S 2 ¯
k = s ¯ 2 S 2 ¯
α = l n s ¯ 1 + c 2
β 2 = l n 1 + c 2
c 2 = S 2 ¯ s ¯ 2
s ¯ = sample mean; S 2 ¯ = sample variance.
Table 2. Parameter estimation and GoF for Pearson Type III distribution of spacings for groupings of simulated flow rate (bins of 100 veh/h).
Table 2. Parameter estimation and GoF for Pearson Type III distribution of spacings for groupings of simulated flow rate (bins of 100 veh/h).
Q (veh/h)1002003004005006007008009001000110012001300
k 0.7390.9221.1301.1881.2611.2151.2761.2711.2761.2441.1861.1551.077
λ 8.00 × 10−42.30 × 10−35.10 × 10−38.20 × 10−31.24 × 10−21.65 × 10−22.21 × 10−22.78 × 10−23.50 × 10−24.18 × 10−24.79 × 10−25.60 × 10−26.02 × 10−2
s 0 6.906.385.795.924.575.634.534.574.584.554.524.534.51
1/ λ 1239.57431.32197.99121.8480.3360.7045.2835.9728.5723.9420.8617.8416.62
E D (veh/km) =
1000 / ( k / λ   + s 0 )
1.082.484.366.649.4412.6016.0419.8924.3729.1334.1739.7744.62
E[ s ] (m) =
s 0 + k / λ
922.73403.91229.49150.62105.8979.3662.3350.2841.0334.3329.2725.1522.41
D n ¯ 0.1140.1120.1020.1000.1020.1000.1040.1030.1030.1070.1110.1140.117
Mean p Value0.260.260.340.360.340.350.320.320.310.290.240.220.20
D n ¯ < K S C α = 0.05 , n = 100
Mean p Value > 0.05
**************************
** Null hypothesis (empirical vs. theoretical distribution consistency) not rejected.
Table 3. Parameters estimation and GoF for Pearson Type III distribution of spacings for groupings of simulated density (bins of 5 veh/km).
Table 3. Parameters estimation and GoF for Pearson Type III distribution of spacings for groupings of simulated density (bins of 5 veh/km).
D (veh/km)1–55–1010–1515–2020–2525–3030–3535–4040–45
k 0.7421.1731.2741.2761.2801.2431.1861.1841.200
λ 1.50 × 10−39.40 × 10−31.72 × 10−22.47 × 10−23.22 × 10−23.97 × 10−24.59 × 10−25.39 × 10−26.35 × 10−2
s 0 5.795.634.534.574.584.554.524.554.53
1/ λ 686.94106.8958.2440.5331.1025.1621.8118.5615.75
E D (veh/km) =
1000 / ( k / λ   + s 0 )
1.947.6312.7017.7722.5227.9232.9137.7042.67
E[ s ] (m) =
s 0 + k / λ
515.72131.0078.7256.2744.4035.8230.3926.5323.43
D n ¯ 0.1360.1040.1020.1050.1040.1060.1110.1090.106
Mean p Value 0.110.320.330.300.310.290.240.260.27
D n ¯ < K S C α = 0.05 , n = 100
Mean p Value > 0.05
****************
** Null hypothesis (empirical vs. theoretical distribution consistency) not rejected.
Table 4. Parameter estimation and GoF for Pearson Type III distribution of spacings for groupings of simulated density (bins of 1 veh/km).
Table 4. Parameter estimation and GoF for Pearson Type III distribution of spacings for groupings of simulated density (bins of 1 veh/km).
D (veh/km)12345
k 0.7380.8970.94171.1341.127
λ 8.00 × 10−42.00 × 10−32.74 × 10−34.70 × 10−35.60 × 10−3
s 0 6.906.386.376.275.79
1/ λ 1244.00497.57365.53213.15178.01
E D (veh/km) =
1000 / ( k / λ   + s 0 )
1.082.212.854.034.85
E[ s ] (m) =
s 0 + k / λ
925.34452.78350.59247.93206.38
D n ¯ 0.1140.1150.1070.1020.102
Mean p Value0.260.240.300.340.34
D n ¯ < K S C α = 0.05 , n = 100
Mean p Value > 0.05
**********
** Null hypothesis (empirical vs. theoretical distribution consistency) not rejected.
Disclaimer/Publisher’s Note: The statements, opinions and data contained in all publications are solely those of the individual author(s) and contributor(s) and not of MDPI and/or the editor(s). MDPI and/or the editor(s) disclaim responsibility for any injury to people or property resulting from any ideas, methods, instructions or products referred to in the content.

Share and Cite

MDPI and ACS Style

Pompigna, A.; Cantisani, G.; Del Serrone, G. Probabilistic Modeling of Inter-Vehicle Spacing on Two-Lane Roads: Implications for Safety-Oriented and Sustainable Traffic Operations. Sustainability 2026, 18, 2896. https://doi.org/10.3390/su18062896

AMA Style

Pompigna A, Cantisani G, Del Serrone G. Probabilistic Modeling of Inter-Vehicle Spacing on Two-Lane Roads: Implications for Safety-Oriented and Sustainable Traffic Operations. Sustainability. 2026; 18(6):2896. https://doi.org/10.3390/su18062896

Chicago/Turabian Style

Pompigna, Andrea, Giuseppe Cantisani, and Giulia Del Serrone. 2026. "Probabilistic Modeling of Inter-Vehicle Spacing on Two-Lane Roads: Implications for Safety-Oriented and Sustainable Traffic Operations" Sustainability 18, no. 6: 2896. https://doi.org/10.3390/su18062896

APA Style

Pompigna, A., Cantisani, G., & Del Serrone, G. (2026). Probabilistic Modeling of Inter-Vehicle Spacing on Two-Lane Roads: Implications for Safety-Oriented and Sustainable Traffic Operations. Sustainability, 18(6), 2896. https://doi.org/10.3390/su18062896

Note that from the first issue of 2016, this journal uses article numbers instead of page numbers. See further details here.

Article Metrics

Back to TopTop