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Article

Longer Truck to Reduce CO2 Emissions: Study and Proposal Accepted for Analysis in Spain

Escuela de Ingenierías Industriales, Universidad de Valladolid, Paseo Prado de la Magdalena 3-5, 47011 Valladolid, Spain
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Author to whom correspondence should be addressed.
Sustainability 2025, 17(13), 6026; https://doi.org/10.3390/su17136026
Submission received: 7 May 2025 / Revised: 20 June 2025 / Accepted: 26 June 2025 / Published: 30 June 2025
(This article belongs to the Special Issue Green Logistics and Sustainable Economy—2nd Edition)

Abstract

The transport industry in the European Union plays a key role in the economy. However, due to persistent political, social, and technological changes, examining optimization strategies in transportation has become a crucial task to minimize expenditure, promote sustainable solutions, and address environmental degradation concerns. This study analyzes the effectiveness of a new truck trailer design, adapted from existing European models, which improves load capacity through an extended trailer length. The increased length (and, by extension, volume) is expected to reduce the number of vehicles for freight transportation, thereby improving road congestion and reducing environmental impacts, which include GHG emissions and overall carbon footprint. To achieve this objective, a comprehensive analysis of current European regulations on articulated vehicles and road trains was carried out, alongside a review of related case studies implemented or under development across the European Union member states. Additionally, a pilot study was conducted using the proposed 18 m semi-trailer across 14 real-life freight routes involving loads from several suppliers and manufacturers. This study therefore demonstrates the economic benefits and reduction in pollutant emissions related to the extended design and evaluates its impact on road infrastructure conditions, given the total length of 20.55 m.

1. Introduction

The transport industry in the European Union plays a critical role in the economic sector; however, ongoing political, social, and technological changes have made the study of transportation optimization strategies a priority. There are efforts to reduce energy costs, promote sustainable solutions, and address growing societal concerns about environmental impacts [1,2]. One of the main objectives of the European Union’s transport policies, as set out in the White Paper, is to promote clean, safe, and efficient transport [3]. The European Commission also adopted the “European Green Deal”, a strategic framework with a time horizon of up to 2050 to achieve sustainable solutions in transport [4].
In 2015 the United Nations General Assembly made a commitment to the 2030 Agenda, with 17 Sustainable Development Goals (SDGs), as a way of improving the quality of life for countries and their population. Goal number 13 is based on concerns about carbon dioxide (CO2) and other greenhouse gas (GHG) emissions in all countries and the negative consequences both socially and economically [5,6]. Despite increasingly stringent regulations, heavy-duty freight vehicles account for approximately 25% of road transport emissions in the EU and 6% of total greenhouse gas emissions [7,8,9,10,11], which aligns with what is reported by the United States Environmental Protection Agency (EPA) [12].
Consequently, research should be aligned with current social needs, which compel companies to enhance their competitiveness by employing strategies that reduce transportation-specific costs. Simultaneously, these strategies must account for future resource constraints and prioritize environmental sustainability, specifically the reduction of GHG emissions.

1.1. Transport in Europe

There are five main modes of freight transport in the European Union: sea, road, rail, inland waterways, and air. Of these, road transport is the most widely used mode for conveying goods from their origin to their inland destination. According to statistics [13], road transport increased from 2013 to 2023 by 2.8%, making it the transport mode with the most favorable evolution over the last 10 years (Figure 1).
An analysis of road transport share over the past decade across European Union member states, measured in tonne-kilometers, shows a slight decrease in countries like Ireland, Poland, and Portugal. On the contrary, significant increases have been observed in countries like Lithuania, Romania, Latvia, Slovakia, Finland, and Sweden (Figure 2). This translates into growing air pollution emissions, including CO2. Transport costs usually justify the reasons for this state of affairs; road transport of cargo is generally cheaper or more easily available than rail transport. Therefore, the search for new technologies for transporting cargo by road is fully justified.
Considering the distribution of modes of transport by country for the year 2023 presented in Figure 3, Spain’s primary modes of freight transport are sea, road, and rail, with air and inland river routes being uncommon. Amidst these, road transport is the most popular method for inland freight movement, with cargo volumes exceeding 266.5 billion tonne-kilometers [14].

1.2. Load Carried vs. Load Capacity

Efficiency in freight logistics plays a crucial role in the performance of road transport, the primary mode of inland freight movement, yielding both economic and environmental benefits [15,16]. The volume and weight of transported material have a significant influence on transport performance. According to [17] a high percentage of trucks operate at full capacity (volume) without attaining their maximum weight limits, especially in cases involving the transport of large, bulky items with a relatively low mass. The study of truck trailer dimensions (in particular, length) can have an impact on increasing the efficiency of road transport. If the load capacity increases in volume, even if it is not increased in weight, this can result in reducing the number of trips, which translates into a reduction in costs as well as the overall CO2 and GHG emissions [18].
Carrying capacity has been analyzed from different points of view (public sector, private sector, and customers), leading to a wide variety of results, but no standard has been found to calculate the most efficient carrying capacity depending on different uses [18,19,20].
Figure 4 shows the average load, measured in tonnes, calculated by “dividing the annual freight throughput (metric ton-kilometers) by the corresponding loaded distance travelled (vehicle-kilometers, equivalent to kilometers)” [17]. This indicator shows information on the average weight of tonnes transported per kilometer over the total distance traveled with load (excluding empty trips). As shown in the graph, the average load in the European Union in 2023 was 15.7 tonnes, while, at the national level, it was 13.4 tonnes. These data indicate that based on the average load percentage, freight vehicles do not reach the allowed maximum weight, suggesting that load limitations are essentially due to volume constraints [17]. In Spain, a study found that only half of the vehicles with a maximum authorized weight of 40 tonnes exceeded 32 tonnes [14].

1.3. Objective

The objective of this study is to analyze the effectiveness of a new truck trailer design that increases the load capacity in volume (specifically by increasing its length) and is adapted from existing European models or modified for cost-effective implementation. The aim is to demonstrate the potential for reducing transport costs for logistics companies. By increasing volume capacity, the number of vehicles required and the distance traveled can be reduced, which, in turn, can contribute to lowering environmental impacts and decreasing greenhouse gas (GHG) emissions.
To achieve this objective, we first present a brief summary of the latest and most relevant European regulations in terms of weight and volume for articulated vehicles and road trains. Next, we analyze studies of longer trailers already carried out in other European Union countries, mainly Italy and the United Kingdom, before presenting our new proposal: an 18 m trailer (against the current 13.6 m). We then compare the different vehicles currently authorized in the European Union with our proposal for an 18 m trailer, determining their respective advantages and disadvantages in road transport. This article concludes with the most significant findings, limitations of this study, and future research directions.

2. Current Lorry Size and Weight Regulations in Europe

Road safety, environmental protection, and the reduction of GHG emissions have become key aspects when designing weight and length standards for heavy goods vehicles (HGVs) in Europe [1,15,16]. In addition, there are other aspects that are considered when determining the length and weight of trucks, such as the type of goods transported (weight or length), infrastructure characteristics (road width or turning angle), manoeuvrability, and the difficulty of adapting or building new trailers [21,22,23,24].
Although there are some minor differences between member countries, these guidelines and criteria align with the European Union directive [25,26]. Also, the European directive foresees exceptions for those countries that do not belong to the European Union, being able to accommodate vehicles that exceed the stipulated weight, length, height, or width of the truck cabin.
Unlike weight and length, which can be subject to more variations, which will be explained in later sections, the maximum authorized width and height of the truck cab are very harmonized. The maximum authorized height is generally 4 m, with some exceptions, where heights of 4.2 to 4.5 m are allowed. The maximum authorized width is, in most countries, 2.55 m [25].

2.1. Weight Regulations in Europe

European regulations on the maximum permissible weight of goods vehicles vary more than the length in different European countries [25,27]. There are not only notable differences when considering vehicle type (road train and articulated vehicle) but also regarding the number of axles, the type of goods, or the condition of the roads.
As for the articulated vehicle, the maximum permitted weight varies from 40 to 44 tons in most countries, with the exception of Ireland, with a maximum of 46 metric tons; the Czech Republic, which can reach up to 48 metric tons; and some countries, such as the Netherlands and Norway, which reach a maximum of 50 metric tons. In contrast, Armenia has a limit of 36 metric tons, the lowest limit of all European countries.
The road train, depending on whether its configuration is of 4, 5, or more axles, has, in general, minimum and maximum permitted limits of 36 to 40 metric tons, respectively; it can reach 46 metric tons in the case of Ireland, 48 metric tons in the Czech Republic, and up to 50 metric tons in the case of The Netherlands and Norway.

2.2. Length Size Regulations in Europe

Despite the fact that the length of heavy goods vehicles in Europe is fairly uniform, depending on the typology concerned, for articulated vehicles (16.5 m, including tractor units and semi-trailers) or road trains (18.75 m in total, with a payload dimension of 15.65 m), there are specific differences [25,28]. Distinctive variations in the length of articulated vehicles are observed in Nordic Countries, such as Norway (17.50 m), Finland (23 m), and Sweden (24 m), as well as in European countries near the East Asian border such as Azerbaijan and Russia (20 m), Ukraine (22 m), and Belarus (24 m).
The European countries that authorize greater cargo lengths for road trains are the Nordic nations—Norway, Sweden, and Finland—with maximum lengths ranging from 19.50 m to 34.50 m [29,30,31,32,33]. This is primarily due to the use of low-traffic-density roads and the considerable distances between cities. Additionally, Azerbaijan, Belarus, and Russia permit a cargo length of 20 m, while Ukraine allows a greater length, reaching up to 22 m [34].

2.3. Other Studies of Longer Vehicles in Europe

One option to respond to the problem of transport costs and emissions reduction is the development and introduction of longer and heavier vehicles (HLVs) than those set by according to the regulations of the European directive. Among the benefits are reductions in costs per unit load, labor, and GHG emissions, as well as the possibility of improving workers’ skills and increasing their salaries. On the other hand, the disadvantages include high investments in infrastructure [35].
Although the use of longer and heavier vehicles is already in place in European countries, most territories have been implementing this option through pilot tests [36,37,38,39,40,41]. These tests served to ensure a positive impact and reduce potential accidents at the time of implementation.

2.3.1. European Modular System (EMS)

The “European Modular System” (EMS) consists of modules assembled to improve load capacity. This combination of trailers is present in European legislation [25,26,42].
This alternative vehicle configuration, approved in only a limited number of countries, allows for up to five distinct combinations of 25.25 m vehicles (Figure 5). The most common combinations are a 12 m truck with a 13.6 m semi-trailer or a tractor with a 13.6 m semi-trailer and an 8 m trailer. Nevertheless, despite the fact that northern European countries (Finland, Denmark, Sweden, and Norway) and the Netherlands have been utilizing them for over two decades, their usage has only recently been expanded in Germany (in select federal states) and with special permits limiting their use on specific roads in Spain, Portugal, Belgium, and the Czech Republic [43]. This is done with the intention of reducing emissions of CO2 and other particulates [44]. Moreover, while the movement of goods within these countries is permitted for 25.25 m trucks, the tonnage transported varies considerably, from 40–44 to 60 (in Norway and the Netherlands) and even reaching 64 in Sweden. Nevertheless, the utilization of these vehicles has not yet been fully implemented, and trials are ongoing in other countries, such as Poland and Slovakia [45,46].

2.3.2. Progetto DICIOTTO (Italy)

In 2009, a project called “Progetto DICIOTTO” was initiated in Italy and developed by the “Associazione Italiana Filiera Industria Automobilistica” [48] and other companies in the transport industry. The objective was to increase the transport load capacity by increasing only the length of articulated trucks from 16.50 m to 18 m, without extending the weight limit, 44 metric tons (Figure 6).
The conclusions of the experimental phase [48], involved over 300 vehicles and routes from 200 to 600 km, indicated that achieving load saturation in terms of both volume and weight resulted in a 12% reduction in the number of trips; this led to reduced fuel consumption per unit of goods transported and, consequently, achieved lower GHG emissions. As regards driving safety, overtaking, and manoeuvrability, no significant differences were observed between the new trailer design and the traditional vehicles.
The project was concluded with the publication of the “DL Infrastrutture of 10/09/2021”, which permitted the operation of this vehicle type on Italian territory, having demonstrated a reduction in traffic volume due to its capacity to transport 37 Europallets, four more than the previous configuration, without significant impact on daily traffic patterns.

2.3.3. High Volume Semi-Trailers (United Kingdom)

The “Longer Semi-Trailer trial” was initiated in the United Kingdom in 2012 following a proposal from the Ministry of Transport to increase the length of articulated vehicles to a maximum length of 18.75 m while maintaining the same weight limit of 44 metric tons (Figure 7). This approach provided a greater transport of pallets (1 × 1.2 m), from 26 to 30, providing a reduction in the kilometers traveled and, therefore, an economic benefit and reduced environmental impact. The project also aimed to reduce infrastructure costs, traffic accidents, and noise pollution [49].
Once the test routes were completed, the findings were very positive, with one in twelve journeys reduced, CO2 emissions down by 48,000 metric tons, and NOx down by 241 tons. In addition, the trials showed that there were 53% fewer road accidents than the UK HGV average [50,51]. Currently, these vehicles are allowed to circulate until 2027.

2.3.4. Double Trailer Trucks and Other Trials

At present, a number of countries have introduced regulations allowing the operation of double trailer trucks with a maximum length of 32–34.5 m and a gross vehicle weight of up to 74–76 metric tons on certain roads and under specific conditions (depending on the regulations) [30]. Examples include Sweden in 2018 [52] and Finland in 2019 [29,43]. This combined vehicle is composed of a tractor unit followed by two semi-trailers, each measuring 13.6 m in length and equipped with 9 or 10 axles (see Figure 8) and even 11 axles in some cases.
These configurations are currently being tested in countries such as Spain and the Netherlands, initially within automotive companies like Seat and Volkswagen [53]. However, several logistics operators have already extended their experimental use for the transport of other goods. Similarly, other countries, such as Denmark, are contemplating the implementation of these vehicle combinations with the aim of reducing CO2 emissions and transportation costs [54].

3. Description of the Proposed Solution

The proposal for the semi-trailer is to extend the length of the semi-trailer, as has been studied in Italy and the United Kingdom. However, this proposal goes one step further and proposes a maximum total length that road trains carrying cars are allowed. The proposed length of car carrier trucks is 18.75 m plus 1.8 m, which sums up to 20.55 m, as the load is permitted to overhang [26]. Therefore, our proposed total length is identical to that of a road train transporting automobiles, which commonly operates on European roads. Notably, this proposal suggests a semi-trailer longer than those currently in circulation; however, it does not exceed the maximum permitted length for road trains, which are legally authorized to travel on all EU roads without the need for special permits. In accordance with the aforementioned directive, most infrastructure is already adapted to accommodate them.
In Section 3.1. the technical characteristics are explained and, in the following points, the load carrying capacities (Section 3.2) and environmental impacts (Section 3.3) according to the methodology proposed by [31,55] are discussed.

3.1. Technical Specifications of the Proposed Semi-Trailer

Figure 9 illustrates the initial semi-trailer (13.6 m) utilized for the manufacture of the proposed semi-trailer (18 m).
As illustrated in Figure 9, the rear overhang is moderately augmented (1.1 m) as well as the distance from the fifth wheel to the first axle (3.3 m), thereby enabling the length of the semi-trailer to be extended from 13.6 m to 18 m. This conversion was performed by an accredited trailer manufacturer in compliance with all safety and quality standards in vehicle manufacturing.
Initially, the investment required for converting these semi-trailers was undertaken by the transport logistics company itself, as the modifications were based on existing semi-trailers that were slightly extended. The resulting operational savings enabled the investment to pay for itself in under three months.
Table 1 presents the most notable technical specifications with regard to allowable masses (in kilograms) and dimensions (in millimeters) before and after the modification.
To analyze the dynamic behavior of the proposed vehicle, a simulation was previously conducted in accordance with the methodology proposed by [56]. The results were validated by comparing them with the calculated values for vehicles already in operation in the European Union, including articulated trucks, road trains, and EMS vehicles. These data were sourced from the Organization for Economic Co-operation and Development (OECD) report [57]. Table 2 presents the most significant results:
  • Total swept width for the low-speed turning manoeuvre (m). The ability of vehicles to navigate low-speed swept paths is of utmost importance in areas with high traffic density, where traffic circles and narrow intersections are prevalent. Failure to provide sufficient space for manoeuvring can result in dangerous situations. European regulations stipulate that vehicles must be able to complete a 360-degree turning manoeuvre at a speed of 5 km/h while remaining within an area of the roadway delineated by an “inner” circle with a diameter of 7.2 m and an “outer” circle with a diameter of 12.5 m.
  • Total swept width for traveling on a rough road at 90 km/h. The operation of vehicles on uneven road surfaces can also present challenges because of the tendency of the rear trailer to deviate from the track, a phenomenon influenced by the roughness of the road and the resulting impact on the tires and suspension of the vehicle. This lateral movement can potentially pose a hazard to other road users or even result in the rear trailer leaving the paved surface.
  • Lateral acceleration amplification ratio of the hauling unit vs. the trailer. The phenomenon of rearward amplification affects the tendency of a semitrailer to experience greater lateral acceleration than the tractor. It is of great consequence to road safety because lateral acceleration and the resulting “tiling” of the rear trailer can cause the entire vehicle to overturn [58]. A reduction in rearward amplification values will consequently result in a reduction in the risk of rollover.
  • Lateral off-tracking during lane change manoeuvre (m). The lateral deviation of the rear trailer during a lane change manoeuvre is a significant safety concern as it has the potential to endanger other road users. As with the previous measures, reducing the lateral deviation of the rear trailer will enhance the safety of these vehicles during driving manoeuvres.
Considering the data in Table 2, it can be seen that the proposed truck has similar behavior to other vehicles already legally circulating in the European Union. The proposed vehicle has a lateral displacement during the lane change manoeuvre lower than the road train and the EMS, a lateral acceleration ratio of the trailer similar to the articulated vehicle from which it is derived and lower than the road train, and a similar width intermediate between the articulated vehicle and the road train when traveling on rough roads at high speed. It only performs worse at low speeds, requiring between 1.2 and 1.5 m more than existing vehicles, which makes it difficult to manoeuvre in built-up areas with roundabouts and narrow intersections [21,23,59]. In any case, the Spanish Directorate General of Traffic deemed these values appropriate and safe for road use when granting authorization for our proposal.

3.2. Load Capacity

From an economic standpoint, following the evaluation of the proposed truck’s stability and manoeuvrability, it is important to assess the implications of the increased load capacity. Notably, the proposed design does not imply an increase in the total authorized weight of the vehicle. However, the tare weight of the modified semi-trailer is 1800 kg more than the 13.6 m version, resulting in a corresponding reduction of 1800 kg in payload capacity. This may pose a limitation for vehicles that typically operate at maximum weight capacity. However, in practical terms, this is not a significant concern, as only 57% of vehicles on the road are saturated by weight, whereas 92% are limited by volume [55]. Therefore, although its weight capacity does not increase, extending its length (and volume) allows for the transportation of a greater quantity of goods.
Table 3 shows the lengths, areas, and volumes of the most common vehicles in the European Union for national and international transport (articulated vehicle, road train, and EMS) compared to the 18 m extended semi-trailer proposal. It can be seen that our proposal, which is structurally like the 16.5 m articulated vehicle, represents an increase of over 30% in loading capacity in terms of volume. Therefore, all the vehicles that circulate saturated in volume (over 92%) and not saturated in weight (over 57%) could take full or partial advantage of this increase in loading capacity.
Nowadays a huge amount of goods is transported on pallets. In Europe, the standard size of a pallet is 1.2 × 0.8 m. On the basis of these dimensions and considering the necessary clearances, it is possible to transport
  • on a 16.5 m articulated truck (13.6 m semi-trailer), a maximum of 33 pallets (if not stacked high) arranged in 11 rows of 3 pallets or 15 rows of 2 pallets plus one row of 3 pallets;
  • on an 18.75 m road train (truck plus trailer with a maximum loading length of 15.65 m), a maximum of 38 pallets (19 + 19);
  • on a 25.25 m EMS (13.62 semi-trailer plus 7.82 trailer), a maximum of 52 pallets (33 + 19);
  • on the proposed 18 m semi-trailer, a maximum of 44 pallets arranged in 14 rows of 3 pallets and 1 row of 2 pallets (Figure 10) or 22 rows of 2 pallets (Figure 11).

3.3. Environmental Impact

In Europe, today’s trucks are equipped with engines that comply with the Euro VI emissions standards, which represent the most recent and strictest standard implemented in the region. The standard has been in force since 2014 and has set very strict limits to reduce emissions of polluting gases like nitrogen oxide (NOx) and fine particulate matter (PM). The remaining CO2 emissions are directly related to fuel consumption [60,61]. The VECTO simulation software (version 4.3.3) [62], proposed by the European Commission, is used to calculate CO2 emissions. This software implements Regulation (EU) 2017/2400 [63,64] concerning the determination of CO2 emissions and fuel consumption of heavy-duty vehicles. VECTO considers several key factors, such as road characteristics, average speeds across defined road segments, and vehicle load. As a result, it is considered a reliable simulation tool. Its accuracy has been validated by various authors through comparisons with actual emissions measured using onboard equipment [60,65,66]. Due to its reliability, VECTO is widely employed in the assessment of CO2 emissions and is also an essential tool for the certification of new vehicles and technologies [67,68,69,70,71].
While an increase in vehicle dimensions and transported weight leads to higher overall fuel consumption, it simultaneously results in a reduction in fuel consumption per tonne per kilometer [31].
In order to measure the efficiency of different types of trucks, ref. [55] defined a “fuel efficiency index” based on liters consumed per 100 km and pallets transported and a “pallet index” representing “road meters used per pallet”, including a safety distance (considering three alternatives: 70 m, 40 m, and 2½ × truck length). Then, ref. [55] calculated these indices for the different types of trucks most commonly used in the EU: single truck (12 m/26 tonnes), articulated truck/semi-trailer (16.5 m), road train (18.75 m), and EMS (25 m). Table 4 shows these indices and their calculations for our proposed truck.
Therefore, the proposed truck exhibits greater spatial efficiency for pallet transport compared to articulated trucks and road trains, and even surpasses European Modular Systems (EMSs) when considering the required safety distances between moving vehicles. This results in a reduction in both the number of vehicles needed on the road and the total space they occupy, thereby improving traffic flow and alleviating congestion. Furthermore, the proposed design enhances fuel efficiency per pallet, enabling the transport of 44 pallets without a substantial increase in fuel consumption, as the gross vehicle weight remains unchanged.

4. Analyzed Routes and Identified Savings

After conducting simulation-based analyses that confirmed the proposed vehicle’s manoeuvrability and stability and demonstrating increases in load capacity and a reduction in environmental impact—including reduced fuel consumption per pallet and fewer trucks in circulation—the Spanish Directorate General for Traffic (DGT) approved a pilot study of the 18-m semi-trailer across multiple routes, transporting real-world loads from various suppliers and manufacturers.
The initial phase of this study identified fourteen routes between suppliers and manufacturers that were being used with 13.6 m semi-trailers. This data was collected in order to have a basis for comparison with the results that would be obtained with the proposed 18 m semi-trailer. These routes encompassed both conventional two-way roads and motorways, as well as selected roundabouts and intersections. However, the routes were relatively straightforward, as the suppliers and manufacturers were situated in industrial areas and did not utilize roads that interconnected with urban centres.
Table 5 shows the data for the 14 routes proposed for this study. The data for these routes for 16.5 m articulated lorries are average calculations based on the last two years of data between the origin and destination points of each of the routes. The table is arranged according to the total number of trips per year on each of the routes. It was observed that there was one route with an average of over 160 trips per day, but with a very short distance (less than 2 km, as the supplier was practically integrated with the customer), followed by another route with more than 20 trips per day, with a distance of 80 km between the supplier and the manufacturer. Then there was a group of three routes with an average of about ten trips per day, each with a distance of 200–350 km, and another group of routes with six to seven trips per day, with distances of between 125 and 130 km (three routes), 300 km, and up to 550–650 km (three routes). The last route analyzed was the one with an average that was more than a single daily trip of 240 km. This resulted in more than 250 routes being analyzed per day, of which one was very short (2 km), but the rest ranged between 100 and 650 km, with an average distance of 300 km.
Therefore, a wide variety of routes with significantly different lengths and frequencies were evaluated. However, all selected routes shared the characteristic that the trucks were volume-constrained but not weight-constrained due to the nature of the transported goods. This made them particularly suitable for assessing the impact of increasing the semi-trailer’s length—and thus its volumetric capacity—without exceeding the maximum permitted weight limits established in Spain and most other European Union countries.
In Table 5, in addition to the distance data for each route, CO2 emission estimates (in grams) were incorporated using VECTO software. These calculations took into account the specific characteristics of each route, such as gradients, lanes, and vehicle loads. As a result, routes with similar distances could exhibit different CO2 emissions. Nevertheless, a reduction in average emissions of more than 25% could be observed, with decreases ranging between 21% and 30%, depending on the route.
Knowing the number of kilometers traveled and the number of trips per year, the annual costs incurred with these routes were calculated. Naturally, a decrease in the total number of kilometers traveled led to lower fuel consumption, while fewer trips per year resulted in reduced personnel expenses for each route. Finally, when comparing historical data for the 16.5 m articulated trucks with data for the proposed 20.55 m trucks in this study, significant savings were achieved over one year. These reductions, summarized in Table 6, included nearly 15,000 fewer trips, over 1.5 million kilometers saved, almost half a million liters of fuel conserved, more than 1300 tonnes of CO2 avoided, and a financial impact exceeding EUR 2 million.
These arguments were sufficient to persuade the Spanish Directorate General for Traffic to authorize a pilot study involving the proposed 20.55-m vehicle on 14 selected routes. In addition to validating the simulation-predicted outcomes, this study aimed to assess various real-world parameters that were difficult to replicate through modeling. These included the incidence of traffic accidents involving this type of vehicle (both active and passive), occupational risks such as driver stress and physical overexertion, and the potential impact on road infrastructure, including deformations and wear caused by the operation of extended-length trucks.

5. Conclusions

This work allowed us to draw several conclusions. Firstly, the statistics collected for the European Union demonstrated the significance of road transport as a means of land transport to reach the final customer (Figure 1 and Figure 2). Furthermore, these same statistics indicated that the loading percentage of trucks is relatively low, despite the fact that the majority of them are operating at full capacity (Figure 3).
This issue has raised concerns among several European member states, prompting investigations into potential alternatives for the use of longer trucks. Some of these initiatives have led to modifications in European regulations, allowing the operation of 25.25-m trucks [25,26], albeit with specific restrictions, such as special permits or designated roads. However, the proposed configurations involve an increase in the authorized gross weight, necessitating enhanced infrastructure maintenance, as well as a significant rise in the cost of the combined vehicle. This increase, however, is offset by the greater load capacity, ultimately leading to a reduction in the cost per transported tonne.
Secondly, the issue of exceeding existing loading limitations is particularly significant due to the potential incompatibility of infrastructure with increased vehicle weight. Consequently, several countries have conducted studies on longer vehicles while maintaining the maximum permitted gross weight. Notable examples include the Italian study (the DICIOTTO project, ongoing since 2009) [48] and the British study (conducted between 2012 and 2021) [50]. Findings from both studies indicate an increase in semi-trailer length from 13.6 m to 15 and 15.65 m, respectively. These studies reached highly similar conclusions, noting that the vehicles maintained their safety and manoeuvrability while enabling a 15–20 per cent increase in transported volume. As a result, reductions were observed in tCO2 emissions, fuel consumption, and transportation costs per metric tonne.
Similarly, the proposal presented and approved for study by the Spanish Directorate General for Traffic followed a comparable approach: increasing the semi-trailer length from 13.6 m to 18 m (and, consequently, its volume) while maintaining the same gross vehicle weight. This adjustment facilitated the transport of greater freight volumes on routes previously constrained by vehicle size, while preventing further deterioration of infrastructure.
One notable advantage of extending semi-trailers to 18 m, as outlined in this study, is the straightforward conversion of existing 13.6-m models. This modification involves increasing the distance between the fifth wheel and the first axle by 3.3 m and extending the rear overhang by 1.1 m. This approach enables the adaptation of existing semi-trailers to the proposed design without requiring substantial capital investment.
Thirdly, the extension of the semi-trailer to 18 m results in a 30% increase in load capacity (in length and volume) without an increase in the maximum gross vehicle weight. However, as demonstrated in Table 1, there is a slight reduction in load capacity because increasing the size of the semi-trailer also results in an increase in its tare weight. Consequently, the benefits of this proposal are only realized by vehicles that currently carry two thirds of the permitted load and are saturated in volume, as they are able to increase the amount carried in volume without reaching the weight limit.
Finally, increasing the length of semi-trailers and, consequently, the volume that can be transported will reduce the number of vehicles needed to transport the same number of pallets. This implies a reduction in the number of vehicles on the road and a reduction in fuel consumption, CO2 emissions, and cost per pallet transported, as also stated by [31] in their analysis for Sweden. In this proposal, the planned study of the 14 routes revealed reductions of more than 25% in CO2 emissions and fuel consumption and approximately 15% cost savings for the same quantities compared to the previous situation when transporting using 13.6 m semi-trailers.
Additionally, it is important to note that the proposed solution is particularly well-suited for transporting light cargo. This aligns with current trends, as approximately 70% of trucks operating in Europe [57] reach their available volume capacity before reaching the permitted weight limits. The proposed solution introduces a new semi-trailer concept built upon existing models already in use within the European Union for road freight transport. Extending semi-trailers to 18 m enables the development of a more sustainable and scalable transport model, contributing to a reduced environmental footprint of freight transport by lowering CO2 emissions and minimizing resource consumption, without requiring modifications to existing infrastructure.
Despite the promising outlook for implementing the proposed semi-trailer, it is important to acknowledge certain limitations within this study. These may be addressed in future research, provided that operational permits are extended by the Spanish Directorate General for Traffic (DGT). Firstly, the conclusions that could be drawn over 12 months (on 14 routes) may be affected in the future by different demand conditions. Also, this study was carried out with car manufacturers and suppliers, although the results should be stable as long as we have trucks that are saturated in volume and do not reach two thirds of the maximum permitted load. Additionally, the present study lies in its scope, which does not extend to the consideration of regulatory costs in certain European Union countries that impose restrictions on the circulation of specific vehicle types based on road classification, although such costs are not currently in place in Spain.
In line with the identified limitations of this study, future research should focus on extending the study period, drawing upon similar initiatives such as the three-year trial in the United Kingdom and the ten-year study in Italy. Expanding the scope to encompass a greater number of routes with diverse geographical characteristics and a wider range of transported products would also enable a more robust validation of the benefits observed thus far.

Author Contributions

Conceptualization, A.G.; methodology, A.G. and Y.P.; validation, A.G., J.L.E. and Y.P.; formal analysis, A.G., J.L.E. and Y.P.; investigation, J.L.E. and Y.P.; resources, A.G.; data curation, A.G. and Y.P.; writing—original draft preparation, A.G. and Y.P.; writing—review and editing, Y.P. and J.L.E.; visualization, Y.P.; supervision, A.G.; project administration, J.L.E. All authors have read and agreed to the published version of the manuscript.

Funding

This research received no external funding.

Data Availability Statement

The original contributions presented in this study are included in the article. Further inquiries can be directed to the corresponding author.

Acknowledgments

We appreciate the discussions with the drivers of the trucks used in this study and the facilities provided by company managers (who prefer to remain anonymous). We also wish to acknowledge the contributions made by those attending the ICQIS conference in Aveiro.

Conflicts of Interest

The authors declare no conflicts of interest.

References

  1. Atkins, R.; Gianiodis, P. An investigation at the intersection of the sharing economy and supply chain management: A strategic perspective. Int. J. Logist.-Res. Appl. 2022, 25, 1425–1443. [Google Scholar] [CrossRef]
  2. Bowersox, D.J.; Closs, D.J.; Stank, T.P. Ten mega-trends that will revolutionize supply chain logistics. J. Bus. Logist. 2000, 21, 1–16. [Google Scholar]
  3. European Commission. WHITE PAPER Roadmap to a Single European Transport Area—Towards a Competitive and Resource Efficient Transport System. Directorate-General for Mobility and Transport. 2011. Available online: https://eur-lex.europa.eu/legal-content/EN/TXT/PDF/?uri=CELEX:52011DC0144 (accessed on 30 April 2025).
  4. European Commission. The European Green Deal. 2020. Available online: https://eur-lex.europa.eu/legal-content/EN/TXT/PDF/?uri=CELEX:52019DC0640 (accessed on 30 April 2025).
  5. Pino, Y.; Pascual, J.A.; Awodele, I.A. Road Freight Transport in Europe: Alternatives for Increasing Capacity. In Quality Innovation and Sustainability. ICQUIS 2022; de Oliveira Matias, J.C., Oliveira Pimentel, C.M., Gonçalves dos Reis, J.C., Costa Martins das Dores, J.M., Santos, G., Eds.; Springer Proceedings in Business and Economics; Springer: Cham, Switzerland, 2022; pp. 49–61. [Google Scholar] [CrossRef]
  6. Stenico de Campos, R.; Tadeu Simon, A.; de Campos Martins, F. Assessing the impacts of road freight transport on sustainability: A case study in the sugar-energy sector. J. Clean. Prod. 2019, 220, 995–1004. [Google Scholar] [CrossRef]
  7. Christopher, M. Logistics and Supply Chain Management: Strategies for Reducing Cost and Improving Service, 2nd ed.; Pitman Publishing: London, UK, 1999. [Google Scholar]
  8. Enarsson, L. Evaluation of suppliers: How to consider the environment. Int. J. Phys. Distrib. Logist. Manag. 1998, 28, 5–17. [Google Scholar] [CrossRef]
  9. Rogers, M.; Weber, W.L. Evaluating CO2 emissions and fatalities tradeoffs in truck transport. Int. J. Phys. Distrib. Logist. Manag. 2011, 41, 750–767. [Google Scholar] [CrossRef]
  10. European Commission. Heavy-Duty Vehicles. Available online: https://climate.ec.europa.eu/eu-action/transport-decarbonisation/road-transport/heavy-duty-vehicles_en (accessed on 12 June 2025).
  11. Gialos, A.; Zeimpekis, V.; Madas, M.; Papageorgiou, K. Calculation and Assessment of CO2e Emissions in Road Freight Transportation: A Greek Case Study. Sustainability 2022, 14, 10724. [Google Scholar] [CrossRef]
  12. United States Environmental Protection Agency. Carbon Pollution from Transportation. Available online: https://www.epa.gov/transportation-air-pollution-and-climate-change/carbon-pollution-transportation (accessed on 12 June 2025).
  13. Eurostat. Freight Transport Statistics—Modal Split. 2024. Available online: https://ec.europa.eu/eurostat/statistics-explained/index.php?title=Freight_transport_statistics_-_modal_split (accessed on 30 April 2025).
  14. Ortega, A.; Vassallo, J.M.; Guzmán, A.F.; Pérez-Martínez, P.J. Are Longer and Heavier Vehicles (LHVs) Beneficial for Society? A Cost Benefit Analysis to Evaluate their Potential Implementation in Spain. Transp. Rev. 2014, 34, 150–168. [Google Scholar] [CrossRef]
  15. Chatti, W. Moving towards environmental sustainability: Information and communication technology (ICT), freight transport, and CO2 emissions. Heliyon 2021, 7, e08190. [Google Scholar] [CrossRef]
  16. Sperling, D.; Salon, D. Transportation in Developing Countries: An Overview of Greenhouse Gas Reduction Strategies; UCD-ITS-RP-02-11; Institute of Transportation Studies, University of California, Davis: Davis, CA, USA, 2002; Available online: https://itspubs.ucdavis.edu/publication_detail.php?id=327 (accessed on 30 April 2025).
  17. Eurostat. Road Freight Transport by Journey Characteristic—Statistics Explained. 2024. Available online: https://ec.europa.eu/eurostat/statistics-explained/index.php?title=Road_freight_transport_by_journey_characteristics (accessed on 30 April 2025).
  18. Abate, M. Determinants of capacity utilisation in road freight transportation. J. Transp. Econ. Policy 2014, 48, 137–152. [Google Scholar]
  19. Abate, M.A.; Kveiborg, O. Capacity utilisation of vehicles for road freight transport. In Freight Transport Modelling; Ben-Akiva, M., Meersman, H., Van de Voorde, E., Eds.; Emerald: Leeds, UK, 2013; pp. 281–298. [Google Scholar] [CrossRef]
  20. Piecyk, M.I. Analysis of Long-Term Freight Transport, Logistics and Related CO2 Trends on a Business-as-Usual Basis. Ph.D. Dissertation, Heriot-Watt University, Edinburgh, UK, 2010. [Google Scholar]
  21. Amoruso, F.; Cebon, D. Brake-actuated steering control strategy for turning of articulated vehicles. Veh. Syst. Dyn. 2025, 63, 424–454. [Google Scholar] [CrossRef]
  22. Anderson, J.E.; Van Wincoop, E. Trade costs. J. Econ. Lit. 2004, 42, 691–751. [Google Scholar] [CrossRef]
  23. Castillo-Manzano, J.I.; Castro-Nuño, M.; Fageda, X. Analyzing the safety impact of longer and heavier vehicles circulating in the European market. J. Saf. Res. 2021, 77, 1–12. [Google Scholar] [CrossRef]
  24. Rodrigue, J.P. The Geography of Transport Systems, 5th ed.; Routledge: London, UK, 2020. [Google Scholar]
  25. Directive (EU) 2015/719 of the European Parliament and of the Council of 29 April 2015 Amending Council Directive 96/53/EC Laying Down for Certain Road Vehicles Circulating Within the Community the Maximum Authorised Dimensions in National and International Traffic and the Maximum Authorised Weights in International Traffic (Text with EEA relevance). Off. J. 2015, 115, 1–10. Available online: http://data.europa.eu/eli/dir/2015/719/oj (accessed on 30 April 2025).
  26. Council Directive 96/53/EC Laying Down for Certain Road Vehicles Circulating Within the Community the Maximum Authorized Dimensions in National and International Traffic and the Maximum Authorized Weights in International Traffic. Off. J. 1996, 235, 59–75. Available online: http://data.europa.eu/eli/dir/1996/53/oj (accessed on 30 April 2025).
  27. ITF. Permissible Maximum Weights of Lorries in Europe, International Transport Forum Organization. 2022. Available online: https://www.itf-oecd.org/permissible-maximum-weights-lorries-europe (accessed on 30 April 2025).
  28. ITF. Permissible Maximum Dimensions of Lorries in Europe, International Transport Forum Organization. 2022. Available online: https://www.itf-oecd.org/permissible-maximum-dimensions-lorries-europe (accessed on 30 April 2025).
  29. Liimatainen, H.; Pöllänen, M.; Nykänen, L. Impacts of increasing maximum truck weight–case Finland. Eur. Transp. Res. Rev. 2020, 12, 14. [Google Scholar] [CrossRef]
  30. Palander, T. The environmental emission efficiency of larger and heavier vehicles e A case study of road transportation in Finnish forest industry. J. Clean. Prod. 2017, 155, 57–62. [Google Scholar] [CrossRef]
  31. Pålsson, H.; Winslott Hiselius, L.; Wandel, S.; Khan, J.; Adell, E. Longer and heavier road freight vehicles in Sweden: Effects on tonne-and vehicle-kilometres, CO2 and socio-economics. Int. J. Phys. Distrib. Logist. Manag. 2017, 47, 603–622. [Google Scholar] [CrossRef]
  32. Björk, L.; Vierth, I.; Cullinane, K. Freight modal shift: A means or an objective in achieving lower emission targets? The case of Sweden. Transp. Policy. 2023, 142, 125–136. [Google Scholar] [CrossRef]
  33. Huang, W.; Ahmadian, M.; Rahimi, A.; Steiginga, L. Dynamics performance of long combination vehicles with active control systems. Veh. Syst. Dyn. 2023, 61, 1831–1880. [Google Scholar] [CrossRef]
  34. Rostislav, K.; Ponomarev, Y. Russia’s Transportation Complex in 2023. Available online: https://papers.ssrn.com/sol3/papers.cfm?abstract_id=4932398 (accessed on 30 April 2025).
  35. Lindqvist, D.; Salman, M.; Bergqvist, R. A cost benefit model for high capacity transport in a comprehensive line-haul network. Eur. Transp. Res. Rev. 2020, 12, 60. [Google Scholar] [CrossRef]
  36. Liimatainen, H.; Greening, P.; Dadhich, P.; Keyes, A. Possible impact of long and heavy vehicles in the United Kingdom—A commodity level approach. Sustainability 2018, 10, 2754. [Google Scholar] [CrossRef]
  37. Meers, D.; Van Lier, T.; Macharis, C. Longer and heavier vehicles in Belgium: A threat for the intermodal sector? Transp. Res. Part D Transp. Environ. 2018, 61, 459–470. [Google Scholar] [CrossRef]
  38. Pålsson, H.; Sternberg, H. LRN 2016 SPECIAL–high capacity vehicles and modal shift from rail to road: Combining macro and micro analyses. Int. J. Logist. Res. Appl. 2018, 21, 115–132. [Google Scholar] [CrossRef]
  39. Sanchez Rodrigues, V.; Piecyk, M.; Mason, R.; Boenders, T. The longer and heavier vehicle debate: A review of empirical evidence from Germany. Transp. Res. Part D Transp. Environ. 2015, 40, 114–131. [Google Scholar] [CrossRef]
  40. Seidenova, U.; Hundenborn, J.; Keuchel, S. Costs and capabilities of innovative concepts of long and heavy vehicles in Germany. Res. Transp. Bus. Manag. 2022, 44, 100518. [Google Scholar] [CrossRef]
  41. Vierth, I.; Lindgren, S.; Lindgren, H. Vehicle weight, modal split, and emissions—An ex-post analysis for Sweden. Sustainability 2018, 10, 1731. [Google Scholar] [CrossRef]
  42. Directive 2002/7/EC of the European Parliament and of the Council of 18 February 2002 Amending Council Directive 96/53/EC Laying Down for Certain Road Vehicles Circulating Within the Community the Maximum Authorised Dimensions in National and International Traffic and the Maximum Authorised Weights in International Traffic. Off. J. 2002, 67, pp. 47–49. Available online: http://data.europa.eu/eli/dir/2002/7/oj (accessed on 30 April 2025).
  43. Dzioba, A.; Markiewicz, M.; Gutsche, J. Analysis of modular transport systems functioning in selected European countries. In MATEC Web of Conferences, Proceedings of the 19th International Conference Diagnostics of Machines and Vehicles “Hybrid Multimedia Mobile Stage”, Bydgoszcz, Poland, 15–16 December 2020; EDP Sciences: Les Ulis, France, 2021; Volume 332, p. 01008. [Google Scholar] [CrossRef]
  44. Dzioba, A.; Markiewicz, M.; Gutsche, J.; Talaśka, A. Ecological conditions for the implementation of the european modular systems in road transport. In MATEC Web of Conferences, Proceedings of the 20th International Conference Diagnostics of Machines and Vehicles “Hybrid Multimedia Mobile Stage”, Bydgoszcz, Poland, 1–2 December 2021; EDP Sciences: Les Ulis, France, 2021; Volume 351, p. 01022. [Google Scholar] [CrossRef]
  45. Jagelčák, J.; Kiktová, M.; Frančák, M.; Marienka, P. The possibilities of using longer and heavier vehicle combinations in Slovakia. Transp. Res. Procedia 2019, 40, 271–278. [Google Scholar] [CrossRef]
  46. Muślewski, Ł.; Lewalski, M.; Woropay, M. Analysis and evaluation of application of car modular systems in polish road transport. J. KONES 2015, 22, 211–220. [Google Scholar] [CrossRef]
  47. The Danish Road Directorate. Evaluation of Trial with European Modular System. Final Report. 2011. Available online: https://www.vejdirektoratet.dk/sites/default/files/2019-08/Evaluation%20of%20Trial%20with%20European%20Modular%20System%20%20-%20incl.%20appendixes.pdf (accessed on 30 April 2025).
  48. Musso, A. Progetto Diciotto—Long Vehicle Test. Monitoraggio Della Sperimentazione 2° Report Fase II; Paper Presentation; Transpotec Logitec: Verona, Italy, 2019. [Google Scholar]
  49. Department for Transport. Longer Semi-Trailer Feasibility Study and Impact Assessment; Department for Transport: London, UK, 2010. Available online: https://assets.publishing.service.gov.uk/media/5a79ecbee5274a684690d151/report.pdf (accessed on 30 April 2025).
  50. Department for Transport. Ending the Longer Semi-Trailer Trial: Consultation Response; Department for Transport: London, UK, 2021. Available online: https://assets.publishing.service.gov.uk/media/611f8ad6e90e070543723037/ending-the-longer-semi-trailer-trial-consultation-response.pdf (accessed on 30 April 2025).
  51. Department for Transport. Longer Semi-Trailer Trial: 2021 Annual Report; Department for Transport: London, UK, 2023. Available online: https://assets.publishing.service.gov.uk/media/6463a239d3231e001332da8d/longer-semi-trailer-annual-report-2021.pdf (accessed on 30 April 2025).
  52. Behera, A.; Kharrazi, S.; Frisk, E. How do long combination vehicles perform in real traffic? A study using Naturalistic Driving Data. Accid. Anal. Prev. 2024, 207, 107763. [Google Scholar] [CrossRef]
  53. Larrodé, E.; Muerza, V. European Modular Systems performances comparison in freight transport operations. Transp. Res. Procedia 2021, 58, 165–172. [Google Scholar] [CrossRef]
  54. Karam, A.; Reinau, K.H. Evaluating the effects of the a-double vehicle combinations if introduced to a line-haul freight transport network. Sustainability 2021, 13, 8622. [Google Scholar] [CrossRef]
  55. Lumsden, K. Truck Masses and Dimensions—Impact on Transport Efficiency. Department of Logistics and Transportation, Chalmers University of Technology. 2004. Available online: https://www.acea.auto/files/SAG_8_Trucks_Masses__Dimensions.pdf (accessed on 30 April 2025).
  56. Glaeser, K.-P.; Ritzinger, A. Comparison of the Performance of Heavy Vehicles Results of the OECD Study: ‘Moving Freight with Better Trucks’. Procedia Soc. Behav. Sci. 2012, 48, 106–120. [Google Scholar] [CrossRef]
  57. ITF. Moving Freight with Better Trucks: Improving Safety, Productivity and Sustainability; ITF Research Reports; OECD Publishing: Paris, France, 2011. [CrossRef]
  58. Esmaeili, N.; Kazemi, R.; Tabatabaei Oreh, S.H. An adaptive sliding mode controller for the lateral control of articulated long vehicles. Proc. Inst. Mech. Eng. Part K-J. Multi-Body Dyn. 2019, 233, 487–515. [Google Scholar] [CrossRef]
  59. Mohammed, O.; Gonzalez, A.; Cantero, D. Dynamic impact of heavy long vehicles with equally spaced axles on short-span highway bridges. Balt. J. Road Bridge Eng. 2018, 13, 1–13. [Google Scholar] [CrossRef]
  60. Fontaras, G.; Grigoratos, T.; Savvidis, D.; Anagnostopoulos, K.; Luz, R.; Rexeis, M.; Hausberger, S. An experimental evaluation of the methodology proposed for the monitoring and certification of CO2 emissions from heavy-duty vehicles in Europe. Energy 2016, 102, 354–364. [Google Scholar] [CrossRef]
  61. Meyer, T. Decarbonizing road freight transportation–A bibliometric and network analysis. Transp. Res. Part D Transp. Environ. 2020, 89, 102619. [Google Scholar] [CrossRef]
  62. European Commission. Vehicle Energy Consumption calculation Tool—VECTO. Available online: https://climate.ec.europa.eu/eu-action/transport-decarbonisation/road-transport/vehicle-energy-consumption-calculation-tool-vecto_en (accessed on 30 April 2025).
  63. Commission Regulation (EU) 2017/2400 of 12 December 2017 Implementing Regulation (EC) No 595/2009 of the European Parliament and of the Council as Regards The Determination of the CO2 Emissions and Fuel Consumption of Heavy-Duty Vehicles and Amending Directive 2007/46/EC of the European Parliament and of the Council and Commission Regulation (EU) No 582/2011. Off. J. Eur. Union L 2017, 349, 1–247. Available online: http://data.europa.eu/eli/reg/2017/2400/oj (accessed on 30 April 2025).
  64. Commission Regulation (EU) 2025/258 of 7 February 2025 Amending Regulation (EU) 2017/2400 as Regards the Determination of the CO2 Emissions and Fuel Consumption of Medium and Heavy Lorries and Heavy Buses and the Inclusion of Vehicles Running on Hydrogen and Other New Technologies and Amending Regulation (EU) No 582/2011 as Regards the Applicable rules on the Determination of CO2 Emissions and Fuel Consumption in Order to Obtain an Extension to an EU Type-Approval. Off. J. Eur. Union 2025, 258. Available online: https://data.europa.eu/eli/reg/2025/258/oj (accessed on 30 April 2025).
  65. Rodríguez, F.; Delgado, O. The Future of VECTO: CO2 Certification of Advanced Heavy-Duty Vehicles in the European Union. International Council on Clean Transportation Europe. White Paper. 2019. Available online: https://theicct.org/sites/default/files/publications/Future_of_VECTO_CO2_certification_20191009.pdf (accessed on 30 April 2025).
  66. Binboğa, F. VECTO Review: Reducing CO2 emissions from heavy duty vehicles. Eng. Perspect. 2022, 1, 7–12. [Google Scholar] [CrossRef]
  67. Djordjevic, B.; Ghosh, B. Estimation of Emissions and Fuel Consumption from Irish HDVs using VECTO tool. Transp. Res. Proc. 2023, 72, 3825–3831. [Google Scholar] [CrossRef]
  68. Middela, M.S.; Mane, A.; Djordjevic, B.; Ghosh, B. Greenhouse gas emissions from heavy-duty vehicles in Ireland. Transp. Res. D Trans. Environ. 2024, 130, 104156. [Google Scholar] [CrossRef]
  69. Chong, Y.; Jiang, H.; Li, G.; Guan, M.; Wang, Y.; Yin, H. Research Progress on CO2 Emission Simulation for Heavy-Duty Commercial Vehicles. Sustainability 2025, 17, 2909. [Google Scholar] [CrossRef]
  70. Witham, G.; Swierc, D.; Rozum, A.; Eckstein, L. Innovative Methodology for Generating Representative Driving Profiles for Heavy-Duty Trucks from Measured Vehicle Data. World Electr. Veh. J. 2025, 16, 71. [Google Scholar] [CrossRef]
  71. Zacharof, N.; Broekaert, S.; Grigoratos, T.; Bitsanis, E.; Fontaras, G. A real world assessment of European medium-duty vehicle emissions and fuel consumption. Atmos. Environ. X 2025, 25, 100307. [Google Scholar] [CrossRef]
Figure 1. Modal split of freight transport, EU, 2013–2023, % based on tonne-kilometers [13].
Figure 1. Modal split of freight transport, EU, 2013–2023, % based on tonne-kilometers [13].
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Figure 2. Share of road in total freight transport, 2013 and 2023, % based on tonne-kilometers [13].
Figure 2. Share of road in total freight transport, 2013 and 2023, % based on tonne-kilometers [13].
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Figure 3. Modal split of freight transport, 2023, % based on tonne-kilometers [13].
Figure 3. Modal split of freight transport, 2023, % based on tonne-kilometers [13].
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Figure 4. Average loads of road freight transport by type of operation, 2023, in tonnes [17].
Figure 4. Average loads of road freight transport by type of operation, 2023, in tonnes [17].
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Figure 5. Types of European Modular System (EMS) vehicles [47].
Figure 5. Types of European Modular System (EMS) vehicles [47].
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Figure 6. Differences between “Progetto DICIOTTO” and the traditional truck [48].
Figure 6. Differences between “Progetto DICIOTTO” and the traditional truck [48].
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Figure 7. Differences between the “High Volume Semi-Trailer” and the traditional truck [49].
Figure 7. Differences between the “High Volume Semi-Trailer” and the traditional truck [49].
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Figure 8. DUO trailer with 9 axles (up) and 10 axles (bottom).
Figure 8. DUO trailer with 9 axles (up) and 10 axles (bottom).
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Figure 9. Semi-trailer before (13.6 m) (up) and after (18 m) (down) the proposed transformation.
Figure 9. Semi-trailer before (13.6 m) (up) and after (18 m) (down) the proposed transformation.
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Figure 10. Pallet placement on a 13.6 m semi-trailer vs. the proposed 18 m semi-trailer. Configuration 1.
Figure 10. Pallet placement on a 13.6 m semi-trailer vs. the proposed 18 m semi-trailer. Configuration 1.
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Figure 11. Pallet placement on a 13.6 m semi-trailer vs. the proposed 18 m semi-trailer. Configuration 2.
Figure 11. Pallet placement on a 13.6 m semi-trailer vs. the proposed 18 m semi-trailer. Configuration 2.
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Table 1. Most relevant technical characteristics before and after the proposed transformation.
Table 1. Most relevant technical characteristics before and after the proposed transformation.
BeforeAfter
Tare weight7200 kg9000 kg
M 1/MAM 242,000/36,000 kg42,000/35,000 kg
m 3/MAM axle 19000/8000 kg9000/8000 kg
m/MAM axle 29000/8000 kg9000/8000 kg
m/MAM axle 39000/8000 kg9000/8000 kg
mcp 4/MAM kingpin15,000/12,000 kg15,000/12,000 kg
Number and size of tires6 × 445/45 R19.56 × 445/45 R19.5
Total height4000 mm4000 mm
Total width2550 mm2550 mm
Maximum length13,920 mm18,340 mm
Rear overhang2820 mm3940 mm
Axle spacing 1–21360 mm1360 mm
Axle spacing 2–31360 mm1360 mm
Fifth wheel lead9180 mm12,480 mm
1 M: technically permissible maximum laden mass. 2 MAM: maximum authorized mass or gross vehicle weight (GVW). 3 m: technically permissible maximum mass on the axle. 4 mcp: technically permissible maximum mass at the coupling point.
Table 2. Most relevant results in manoeuvrability and stability.
Table 2. Most relevant results in manoeuvrability and stability.
Type of TruckTotal Swept Width (m)Lateral
Acceleration
Amplification
Ratio
Lateral Off-Tracking During
Lane Change
Manoeuvre (m)
For 5 km/h
Turning
Manoeuvre
Traveling on
a Rough Road
at 90 km/h
Articulated truck (16.5 m)62.871.20.38
Road train (18.75 m)5.782.951.390.89
EMS (25.25 m)6.062.970.910.67
Proposed truck (20.55 m)7.272.971.210.51
Table 3. Comparison of lengths of current EU vehicles vs. proposed truck.
Table 3. Comparison of lengths of current EU vehicles vs. proposed truck.
Articulated Truck
(16.5 m)
Road Train
(18.75 m)
EMS
(25.25 m)
Proposed Truck
(20.55 m)
Semi-trailer length (m)13.6215.6521.4418
Increase (m)/% 2.03/14.90%7.82/57.42%4.38/32.16%
Semi-trailer length (m)33.7838.8153.1744.64
Increase (m)/% 5.03/14.90%19.39/57.42%10.86/32.16%
Semi-trailer length (m)99.31114.11156.32131.24
Increase (m)/% 14.80/14.90%57.02/57.42%31.94/32.16%
Table 4. “Road efficiency index” and “Fuel efficiency index”.
Table 4. “Road efficiency index” and “Fuel efficiency index”.
Type of Truck “Pallet Index” “Fuel Index”
At 70 m
Safety Distance
At 40 m
Safety Distance
At Safety Distance =
2.5 × Truck Length
Articulated truck (16.5 m)
(33 pallets/truck)
(16.5 + 70)/33(16.5 + 40)/33(16.5 + 2.5 × 16.5)/3332/33
2.621.711.750.97
Road train (18.75 m)
(38 pallets/truck)
(18.75 + 70)/38(18.75 + 40)/38(18.75 + 2.5 × 18.75)/3835/38
2.341.551.730.92
EMS (25.25 m)
(52 pallets/truck)
(25.25 + 70)/52(25.25 + 40)/52(25.25 + 2.5 × 25.25)/5242/52
1.831.251.700.81
Proposed truck (20.55 m)
(44 pallets/truck)
(20.55 + 70)/44(20.55 + 40)/44(20.55 + 2.5 × 20.55)/4434/44
2.061.381.630.77
Table 5. Planned routes to compare transport by articulated truck (16.5 m) and proposed truck (20.55 m).
Table 5. Planned routes to compare transport by articulated truck (16.5 m) and proposed truck (20.55 m).
RoutesKm/TripArticulated Truck (16.5 m)Proposed Truck (20.55 m)
Trips/DayTrips/Yearkm/YeargCO2 EmissionsTrips/DayTrips/Yearkm/YeargCO2 Emissions
Route 11.91166.336,59169,87668,665,778123.827,24552,02949,248,306
Route 280.1722.64964397,959385,874,68116.83696296,316268,055,683
Route 3334.9310.62324778,378526,848,1997.91730579,572409,978,926
Route 4357.829.42060737,100631,637,3907.01534548,837451,427,066
Route 5211.898.61901402,797362,273,7876.41416299,918256,397,648
Route 6549.827.21584870,912584,875,2485.41180648,472423,064,637
Route 7644.157.115691,010,678995,419,3305.31168752,540783,802,472
Route 8129.757.01532198,778167,887,8535.21141148,008118,849,779
Route 9294.006.01320388,080364,207,4214.5983288,960252,526,220
Route 10133.605.91294172,872156,467,6584.4964128,719116,727,773
Route 11582.865.81268739,066570,240,9784.3944550,300444,369,360
Route 12126.865.11114141,32697,240,4923.8829105,23074,462,555
Route 13216.683.6792171,612165,784,8762.7590127,781117,098,804
Route 14240.051.329169,85569,480,2591.021752,01348,218,713
104.93266.458,6046,149,2895,146,903,950198.443,6374,578,6953,814,227,941
Table 6. Summary of reductions.
Table 6. Summary of reductions.
Truck 16.5 mTruck 20.55 mEstimated Savings
Truck trip 58,60443,63714,967
Kilometers traveled (km)6,149,2894,578,695157,0594
Diesel consumption (L)1,844,7791,366,860477,919
CO2 emissions (tCO2)514738141333
Transport cost (EUR)13,943,93011,940,0422,003,888
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MDPI and ACS Style

Pino, Y.; Elorduy, J.L.; Gento, A. Longer Truck to Reduce CO2 Emissions: Study and Proposal Accepted for Analysis in Spain. Sustainability 2025, 17, 6026. https://doi.org/10.3390/su17136026

AMA Style

Pino Y, Elorduy JL, Gento A. Longer Truck to Reduce CO2 Emissions: Study and Proposal Accepted for Analysis in Spain. Sustainability. 2025; 17(13):6026. https://doi.org/10.3390/su17136026

Chicago/Turabian Style

Pino, Yesica, Juan L. Elorduy, and Angel Gento. 2025. "Longer Truck to Reduce CO2 Emissions: Study and Proposal Accepted for Analysis in Spain" Sustainability 17, no. 13: 6026. https://doi.org/10.3390/su17136026

APA Style

Pino, Y., Elorduy, J. L., & Gento, A. (2025). Longer Truck to Reduce CO2 Emissions: Study and Proposal Accepted for Analysis in Spain. Sustainability, 17(13), 6026. https://doi.org/10.3390/su17136026

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