"

Chapter 5. Natural Gas Generators

Introduction

Graphic showing gas power plants with a large building in the background
Figure 5.1: Image of a (Combined Cycle Gas Turbine) Natural Gas Power Plant. Credit: Authors created using ChatGPT

Meeting the electric power demands of large loads requires technologies that strike a careful balance between performance, cost, and environmental impact. On-site natural gas generators have emerged as a compelling solution, offering a reliable and efficient means of power generation with the lowest emissions profile among fossil-fueled options. This chapter explores the fundamentals of natural gas generator technology and examines how these systems meet the stringent criteria for large-load applications. Natural gas can be used in both primary and backup generator configurations, providing flexibility for a range of operational needs. With a favorable capital cost structure and consistently high operational performance, natural gas generators present a practical and sustainable choice for facilities seeking dependable on-site power. However, a volatile gas market, their reliance on existing pipeline infrastructure and current supply chain delays for equipment pose risks that must be considered in planning and deployment.

Technology

Several types of electric generator systems fueled by natural gas are currently in service, each suited to specific applications. These include gas-driven piston engines, gas-fired steam engines, single cycle gas turbine (SCGT), combined cycle gas turbine (CCGT) systems (gas turbines coupled with steam turbines), and fuel cells.  Gas turbine and combined cycle generators are the preferred choice for large primary and hybrid power applications due to their high efficiency and scalability, and will be the focus of this chapter. Gas-fired steam engines specialize in niche applications where fuel flexibility is a priority.  Gas-driven piston engines have historically been deployed for backup power, or small systems, and in recent times are not being deployed for 100MW+ peaker plants and data center prime power applications.  While single cycle technologies, generally lack the efficiency desired for large-load primary source applications, they have faster deployment times. Fuel cells represent an emerging technology with promising potential and require further development to become cost-effective and reliable; they will be discussed in a separate chapter.

Gas-fired steam turbines, also known as Rankine cycle systems, use heat from natural gas combustion to produce high-pressure steam that spins a turbine connected to an alternator. This converts thermal energy into mechanical energy, then into electricity through electromagnetic induction. These systems are typically used in industrial or cogeneration settings where both electricity and process heat are needed. While they offer smooth operation and fuel flexibility, their slower start-up times and thermal efficiency—typically 30% to 40%—make them less suitable for dynamic or peak-load applications.

Gas-fired piston combustion engines, or reciprocating engines, operate by compressing a fuel-air mixture in a cylinder and igniting it, usually with a spark plug. The resulting combustion drives a piston, turning a crankshaft connected to an alternator to generate electricity. These engines are valued for their modularity, durability, and efficient performance at partial loads. They are commonly used for backup power and distributed generation due to their quick start-up and relatively low capital cost. Their thermal efficiency—typically 30% to 45%—is higher than gas turbine units, but lower than combined cycle turbine systems.

Gas turbines, in a simple cycle configuration, begin by compressing ambient air, mixing it with natural gas, and igniting the mixture in a combustion chamber. The high-temperature gases expand through a turbine, spinning a shaft that drives both the compressor and an alternator. This process enables rapid start-up and flexible operation, making simple cycle turbines ideal for meeting peak electricity demands. Their thermal efficiency typically ranges from 30% to 35%.

Efficiency can be significantly improved in combined cycle systems, which pair a gas turbine with a steam turbine. Waste heat from the gas turbine’s exhaust is captured in a heat recovery steam generator (HRSG) to produce steam that drives a secondary turbine, generating additional electricity without extra fuel. Combined cycle plants can achieve thermal efficiencies of 55% to 60%, making them ideal for base and intermediate load applications. Though more complex and costly than simple cycle units, they offer superior performance and lower emissions per unit of electricity produced. Common configurations include two combustion turbines paired with one steam turbine (2x1), though variations exist.

The development of simple cycle gas turbines began in the early 20th century, originally adapted from aviation engines for industrial use, and they became widely adopted in the mid-1900s for their ability to provide quick, flexible power generation. Combined cycle technology emerged later, gaining prominence in the 1960s and 1970s as engineers began capturing waste heat from gas turbines to drive steam turbines, significantly improving efficiency and making it a cornerstone of modern power generation. As of recent years, natural gas-fired plants account for over 40% of U.S. electricity generation, underscoring their importance in meeting both base and peak demand.

Simple and combined cycle natural gas turbines continue to evolve, with recent innovations focused on improving efficiency, operational flexibility, and emissions performance. Simple cycle turbines are seeing faster start-up times reaching full load in 10 minutes as compared to 30 minutes on older models. While combined cycle systems benefit from advanced materials and digital optimization offering ramp rates that enable them to quickly adjust output in response to fluctuations in renewable generation. Both are increasingly designed for hydrogen co-firing and carbon capture, supporting long-term decarbonization goals.

1 Deployment Schedule

Deploying natural gas reciprocating, turbines or combined cycle systems for large-scale applications involves the common project phases: development, preconstruction, construction, commissioning, and turnover to operations. CCGTs often require longer schedules than SCGT due to complex heat recovery systems.  While recent federal policy changes have streamlined air permitting, significant challenges persist at the state and local levels. Additionally, the current lead time for procuring a turbine has extended to approximately five years, and constructing new pipelines has a similar timeframe, both posing a major constraint on project timelines that are now in the 6 to 10 years from concept to operation. [1]

Permitting and Regulatory Approvals

Nationwide, permitting and approvals typically take 3 to 12 months, depending on jurisdiction, site-specific environmental regulations, and engineering complexity. Proximity to natural gas pipelines or liquid natural gas (LNG) terminals can expedite timelines, while remote sites may face delays. Permitting for natural gas is similar to other generators, which include Geotechnical studies, Archaeology studies, biological studies, Stormwater studies, and air quality studies.

Interconnection

Natural gas systems have two interconnection processes, one for the gas supply and one for the electricity produced.  The electrical interconnection process is as described in the previous chapters.

Connecting to a natural gas pipeline has a similar process.  It involves a multi-step process that requires coordination between the plant developer, pipeline operator, and regulatory agencies. The key steps include:

  1. Feasibility Study and Route Planning: This involves assessing the proximity of existing natural gas infrastructure, evaluating pipeline capacity, and determining the most efficient and cost-effective route for connection.
  2. Pipeline Interconnection Agreement: The power plant owner must negotiate an agreement with the pipeline operator, which outlines terms for gas delivery, pressure requirements, metering, and operational responsibilities.
  3. Permitting and Environmental Review: Regulatory approvals are required at local, state, and federal levels. This includes environmental impact assessments, right-of-way acquisition, and compliance with safety and emissions standards.
  4. Engineering and Design: Detailed engineering plans are developed for the pipeline lateral, metering station, pressure regulation equipment, and any required compression facilities.
  5. Pipeline Construction and Commissioning: Once permitted, construction of the pipeline lateral and interconnection facilities begins. This includes trenching, welding, testing, and installation of control systems. After construction, the system undergoes commissioning to ensure safe and reliable operation. [2]
  6. Ongoing Operations and Monitoring: After connection, the gas supply is monitored continuously for flow rate, pressure, and quality. Maintenance agreements and emergency response plans are also established.

The time from start of feasibility to final design can take months to years depending on the distance of new pipe and the complexity of associated land control acquisition, tie-in to an existing pipe, and regulatory approvals. Construction times also depend on length and complexity of accommodating for existing rights-of-way.  Testing and commissioning generally take 3 to 8 months.

Alternatives to delivering natural gas by pipelines include cryogenic (-260 degF, -162 degC) liquified natural gas (LNG), or high pressure (3000 to 3600 psig) compressed natural gas (CNG) which are stored in tanks and transported by truck, rail, or barge.  Due to processing and transport, the delivered cost of LNG and CNG is more expensive than pipeline. They can be transported to a site by a natural gas pipeline, and then liquified or compressed for on-site storage.  One work-around for delays in pipeline construction is to start a natural gas power plant with gas delivered as CNG or LNG while waiting for the pipeline to get completed.

Procurement

The global natural gas generator market is led by several major manufacturers that produce systems tailored for industrial, commercial, and utility-scale applications. Key players include GE Vernova (Cambridge, MA)Siemens Energy (Munich, Germany)Mitsubishi Power (Lake Mary, FL), Solar Turbines, a subsidiary of Caterpillar Inc. (San Diego, CA), and Baker Hughes (Florence, Itally). These companies operate manufacturing facilities primarily in the United States, Europe, and parts of Asia, serving both domestic and international demand. For industrial-scale natural gas generators, typical manufacturing lead times range from 10 to 30 weeks, depending on power capacity and customization. However, recent surges in global demand have extended lead times dramatically—up to 7 or 8 years in some cases. [2]

In addition to equipment, securing a fuel supply contract for natural gas generators generally takes 3 to 6 months, influenced by factors such as regulatory approvals, land acquisition, and financing. Gas contracts can be negotiated as having "firm" or "interruptible" delivery. Firm gas is a guaranteed, high-priority service that is not intentionally interrupted, while interruptible gas is a lower-priority service that can be shut off during high demand, in exchange for a lower price. Customers with interruptible service need a backup fuel source, like oil or propane, to switch to when service is interrupted.

Construction and Start-Up

For large-scale deployments of natural gas generators, construction time is influenced by multiple factors, including site preparation, equipment complexity, regulatory compliance, and external conditions. Construction involves extensive groundwork, equipment installation, and system integration, with timelines varying significantly between simple cycle (12–18 months) and combined cycle (18–36 months) plants due to differences in scope and complexity.  Commissioning, start-up, and turnover of fuel supply infrastructure for SCGT and CCGT generators involve inspections, calibrations, and performance testing, typically taking 4–8 weeks, as seen in the Cascade CCGT project (2020–2024). [3] Pressure testing and control logic validation require 2–5 weeks, with CCGT systems needing more time due to HRSG integration. Grid synchronization and emissions testing add 3–6 weeks. [4]  Turnover is delayed by documentation requirements, such as system readiness reports and operator training, which can extend timelines by 1–2 weeks. Total commissioning and turnover time typically span 2–4 months, but complex CCGT projects or stringent regulatory environments may extend this to 5–6 months. [5]

2 Operational Capabilities

Dispatchability and Flexibility

Simple and combined cycle natural gas generators offer varying levels of operational flexibility, particularly when serving large electrical loads.  Simple and combined cycle natural gas generators are highly dispatchable and play a central role in modern grid operations. Simple cycle gas turbines can start and reach full load in under 10 minutes, making them well-suited for peaking applications and fast-response scenarios such as frequency regulation or contingency reserves. Combined cycle systems, while slower to start typically requiring 30 minutes to an hour offer enhanced efficiency and are increasingly designed for flexible operation, including daily cycling and partial load following. Manufacturers provide various unit sizes that can effectively manage loads from 30% to 100% of their rated capacity, with the best performance generally occurring between 70% and 100% of the generator’s continuous rating.   Their ability to modulate output across a wide range of operating conditions makes them valuable assets in both centralized and distributed energy systems.

Start Times and Ramp Rates

Startup times are a critical operational factor for Large industrial SCGTs and CCGTs, as they directly affect the generator’s ability to respond to fluctuations in demand and maintain reliability for large, energy-intensive loads; Table 5.1 below summarizes typical cold start durations for these technologies and highlights their varying capabilities to support rapid grid response.

Table 5.1: SCGTs and CCGTs start times for different modules (Source: [6])
Unit Type Cold Start to Full Load
Heavy Frame SCGT (100–400 MW) 15–30 minutes
Aero‑derivative SCGT (e.g., LM2500) ~5 minutes
OEM F-Class SCGT (M501F) ~30 minutes
CCGT (M501F‑class) ~70 minutes
Generic CCGT ~2.5 hours
Generic CCGT (steam focused) Gas Turbine: 15–30 min;

Steam Turbine: 1– 6 hrs + 20 min –  2 hrs

Ramp rates for SCGTs typically reach 8–12 % capacity per minute, and aeroderivative units may exceed 15%. Ramp rates for CCGT units are slower with a typical range from 2–4 % per minute, with optimized designs pushing up to 8–10 %. [7]

 

Grid Stability and Power Quality

Natural gas generators, including both simple cycle and combined cycle units, contribute to grid stability through integrated control systems. Governor systems regulate turbine or engine speed to maintain grid frequency, while automatic voltage regulators (AVRs) manage output voltage in response to load changes. These generators also provide inertial support, helping buffer short-term frequency fluctuations. Simple cycle gas turbines (SCGTs) typically have an inertia constant (H) ranging from 2 to 4 seconds, while combined cycle gas turbines (CCGTs), which include both gas and steam turbines, benefit from the combined rotating masses, resulting in a higher inertia constant of approximately 4 to 6 seconds. This gives CCGTs a slightly more sustained frequency support capability compared to SCGTs.

Natural gas turbines and combined cycle gas turbines (CCGT) are widely used to supply electric power for large industrial and commercial loads, but they present some power quality challenges that must be addressed to ensure stable operation. These systems can experience voltage fluctuations and frequency instability, particularly during load transitions or startup/shutdown cycles. Harmonics are generally less of a concern with gas turbines compared to inverter-based sources, but they can still arise from auxiliary systems like variable speed drives. To mitigate these issues, operators often deploy AVRs, power factor correction banks, and STATCOMs to stabilize voltage and support reactive power needs. In CCGT systems, the integration of steam turbines can help smooth output and improve efficiency but coordinated control strategies are essential to maintain high power quality across varying load conditions.

Synchronization and Control

Modern natural gas power plants are increasingly designed with modular synchronization systems that allow multiple gas turbines to be brought online in parallel. Generating units typically range from 5 MW to over 300 MW and can be synchronized to the grid using advanced auto-synchronizers and synchronism-check relays that ensure alignment in voltage, frequency, and phase angle before connection. [8] In large-scale applications, such as those involving combined cycle plants, synchronization is critical due to the high-power levels involved and the potential for damaging electrical and mechanical transients if performed incorrectly. The use of droop control allows multiple generators to proportionally share load changes based on their rated capacities, which is essential for maintaining grid stability under varying demand conditions. This coordinated approach ensures that natural gas generators can effectively support large electrical loads, particularly during peak demand or contingency events.

Parasitic Loads and Degradation

Parasitic losses in SCGTs are relatively low, typically between 3% and 5% of rated output, with some aero-derivative designs drawing virtually no parasitic power when idle - if the natural gas is delivered at high pressure (>600 psi). If the natural gas must be compressed, then the parasitic loads can be considerably higher.  Combined cycle gas turbines (CCGTs) require additional auxiliary equipment which contributes to higher parasitic losses, typically ranging from 5% to 8% of rated output. [9]

Natural gas turbines, whether used in simple-cycle or combined-cycle configurations, experience performance degradation over time due to high thermal stresses, material fatigue, and fouling of internal components. Key areas of wear include turbine blades, combustion liners, and hot gas path components, which are exposed to extreme temperatures and corrosive environments. This degradation leads to reduced efficiency, lower power output, and increased fuel consumption if not addressed. To extend service life and maintain performance, turbines undergo periodic refurbishment and overhaul cycles, often guided by equivalent operating hours or starts. These refurbishments may include blade replacement or re-coating, bearing and seal replacement, and advanced non-destructive testing (NDT) to detect cracks or wear. Major overhauls can restore turbines to near-original performance levels and are typically scheduled every 24,000 to 50,000 equivalent operating hours, depending on the manufacturer and duty cycle. In combined-cycle systems, heat recovery steam generators (HRSGs) and steam turbines are also inspected and refurbished in parallel to maintain overall system efficiency and reliability.

3 Service Reliability

Availability and Failures

Turbine blade inspection
Figure 5.2.  Turbine inspection during a 5 year refurbishment. Credit: Authors created using CoPilot.

Natural gas turbines particularly combined cycle gas turbines (CCGT) systems are among the most reliable technologies for delivering consistent, large-scale electricity generation, making them essential for meeting the demands of industrial and utility-scale loads. Natural Gas Generators with regular maintenance have a Mean Time Between Failures (MTBF) ranging from 20,000 to 50,000 hours, indicating reliable operation for extended periods. [10]

Well maintained gas turbines both simple and combined cycle exhibit low failure-to-start rates, typically below 0.5%.  However, poor maintenance or control system faults can increase this rate significantly. Routine maintenance is essential: weekly inspections often include control system diagnostics and fuel system checks, while monthly tasks may involve vibration analysis and thermal imaging. Annual maintenance typically includes borescope inspections, combustion system tuning, and hot gas path component evaluations.

Combined cycle natural gas generators operating in continuous service typically require between 300 and 500 hours of annual maintenance, depending on the manufacturer and operating conditions. This results in a per-unit availability ranging from approximately 94.3% to 96.6%. In contrast, simple cycle gas turbines, often used in peaking or standby roles, require only about 100 to 200 hours of maintenance per year, yielding a higher availability of roughly 97.7% to 98.9%. While these figures suggest high reliability, even modest downtime can pose significant risks when scaled across multiple units in a power system.

In terms of refurbishment, simple cycle gas turbines (SCGTs) typically require a major overhaul or refurbishment every 24,000 to 50,000 operating hours, or roughly every 2,500 to 4,000 starts, depending on their duty cycle. For combined cycle gas turbines (CCGTs), the gas turbine portion generally undergoes major refurbishment on a similar schedule every 32,000 to 50,000 hours, while steam turbine and heat recovery components may require inspection and servicing approximately every 50,000 to 100,000 hours, or every 3 to 5 years in continuous operation. These scheduled refurbishments are in addition to annual maintenance and play a critical role in sustaining long-term reliability and efficiency. [10]

In combined cycle configurations, redundancy extends beyond generator count to include critical plant subsystems. Multi-shaft designs, for example, allow several gas turbines and heat recovery steam generators (HRSGs) to operate in parallel, feeding a common steam turbine. If one gas turbine train experiences a fault, others can continue operating, thereby preserving a significant portion of the plant’s output. In some systems, steam turbines can be decoupled from the gas turbine through a clutch, allowing the gas turbine to operate in simple cycle mode during startup or contingencies.

Redundant & Resilient Architecture

Redundancy is also embedded in plant control systems, where dual programmable logic controllers (PLCs), independent power supplies, and failover mechanisms are used to ensure uninterrupted monitoring and control. Because of the complex operation of a gas turbine, it cannot start without existing electric power.  Some facilities are equipped with black-start capability using diesel generators or battery systems to allow natural gas turbines to start independently of the grid. This is especially important for restoring generation in the event of widespread outages.

External Risks

Simple and combined cycle natural gas generators face a range of external operational risks that can impact reliability and performance. Severe weather events pose direct threats to above-ground infrastructure, limit access to facilities, and disrupt natural gas supply chains. In extreme cold, pipeline freeze-offs and compressor station outages can significantly reduce fuel availability, while heatwaves can impair efficiency by overloading cooling systems and raising intake air temperatures. These generators are also heavily reliant on external infrastructure, such as interstate pipeline networks, compressor stations, and electrical transmission systems. Failures or constraints in any of these can lead to reduced output or complete outages. Additionally, market risks amplify vulnerability: during energy emergencies or peak demand events, natural gas prices can spike sharply, and pipeline capacity may be prioritized for residential heating, leaving generators undersupplied. These risks highlight the need for weatherization retrofits, on-site fuel backup options, and improved regional coordination to ensure grid reliability under high-stress or emergency conditions.

4 Environmental Sustainability

Natural gas turbines are often viewed as a cleaner alternative to coal or diesel generation, offering lower emissions of carbon dioxide (CO₂), nitrogen oxides (NOₓ), and particulate matter. Combined cycle systems, which capture and reuse waste heat, can achieve thermal efficiencies exceeding 60%, further reducing emissions per unit of electricity generated. However, natural gas is still a fossil fuel, and its environmental impact extends beyond combustion. While natural gas plays a key role in grid reliability and transitional decarbonization strategies, its long-term environmental friendliness depends on improvements in leak detection, carbon capture, and clean fuel alternatives.

Emissions & Air Quality Impacts

Natural gas generators emit several key pollutants, including nitrogen oxides (NOₓ), carbon monoxide (CO), and carbon dioxide (CO₂), which contribute to smog formation, respiratory health risks, and global climate change. To address these concerns, modern gas turbines incorporate advanced combustion technologies that significantly reduce emissions. Systems such as dry low-NOₓ (DLN) burners and selective catalytic reduction (SCR) can lower NOₓ emissions by over 90% compared to older, uncontrolled units.

When configured as high-efficiency combined-cycle gas turbines (CCGT), natural gas power plants can emit up to 50% less CO₂ than conventional coal-fired facilities. However, combustion of natural gas still produces greenhouse gases, including CO₂, CO, SO₂, and NOₓ, as outlined in Table 5.2.  According to the U.S. Energy Information Administration (EIA), natural gas combustion for electricity in 2023 accounted for about 37% of total U.S. energy-related CO2 emissions, despite being 36% of energy consumption. [11]

Table 5.2.  Stack Emissions from a Typical Natural Gas Power Plant. [11]
Pollutant Emission Rate (g/MWh) Notes
CO₂ ~370 kg/MWh Varies by efficiency, Carbon capture not included
NOₓ ~.05 – .15 kg/MWh Varies by technology and use of SCR
SOₓ <.001 kg/MWh Very low due to low sulfur content in natural gas
Particulates <.001 kg/MWh Negligible for natural gas combustion
CO ~.01 – .05 kg/MWh Depends on combustion efficiency

Regulatory compliance for natural gas turbines is governed by federal standards, state and local permitting requirements, and regional air quality plans. These frameworks influence project design, siting, and the selection of emissions control technologies. Both simple-cycle and combined-cycle turbines must meet National Ambient Air Quality Standards (NAAQS), especially in nonattainment zones where stricter permitting applies. In such areas, developers may be required to implement Best Available Control Technology (BACT), secure emission offsets, or meet lower NOₓ thresholds set by local authorities.

To further reduce the carbon footprint of gas-fired generation, Renewable Natural Gas (RNG) sourced from biological processes offers a low-carbon alternative, often qualifying for carbon credits. Additionally, emerging technologies such as carbon capture and storage (CCS) are being developed to mitigate CO₂ emissions and enhance the sustainability of natural gas power generation.

Water Use

Natural Gas CCGT and steam turbine power generator plants withdraw on average about 2,800 gallons per MWh of water for cooling and thermal cycling.  Most of that is send to wastewater treatment or disposal, and actual consumption due to evaporation is closer to 200 gallons per MWh for NGCC and 850 gallons per MWh for simple cycle steam turbines.  While natural gas power plants are significantly less water-intensive than coal, they still withdraw substantial volumes of water for cooling, which can strain local aquatic ecosystems.  Water consumption can be reduced with the use of air-cooled fan cooling, however, in hot regions a hybrid cooling system is needed because evaporative cooling is still needed to achieve thermal efficiency with a lower coolant temperature. Natural gas turbines and reciprocating engines do not use water for cooling, however, they may inject some water into the combustion chamber for NOx reduction and steam output boosting.  [12][13][14]

The extraction of natural gas through hydraulic fracturing (fracking) requires millions of gallons of water per well.  On average this translates to 0.6 to 1.8 gallon of water per MMBtu of gas produced, [16] or about 15 gallons per MWh of electricity, which is relatively small compared to the cooling water demand.  An additional environment concern with natural gas production is the large quantities of co-produced wastewater containing salts, heavy metals, radioactive materials, and hazardous chemicals that must be carefully treated or securely stored.  The typical disposal method is deep well injection, but this raises concerns about seismic activity and long-term groundwater contamination.  The industry has addressed many of these issues with improved methods over the past decade.

End of Life Recyclability

Environmental concerns are mild following retirement of a gas power plant.  Decommissioning involves environmental remediation, removal of equipment (turbines and piping), and demolition of infrastructure including buildings and foundations. For combined cycle systems, the dismantling extends to the heat recovery steam generator (HRSG) and steam turbine. The process does not fall under a singular federal regulation and typically follows state and local environmental guidelines. [17] [18]

Hazardous Materials and Waste Management

Natural gas turbines, while cleaner burning than other fossil-fueled generators, still involve a range of hazardous materials that must be properly managed to ensure environmental and workplace safety. Common substances include lubricating oils, coolants, cleaning solvents, and gas compressor lubricants, all of which can pose risks if leaked or mishandled. In combined cycle plants, water treatment chemicals used for boiler and steam system conditioning (e.g., ammonia, phosphates, and oxygen scavengers) also require careful storage and handling. Spills or improper disposal of these substances can contaminate soil or water, triggering environmental violations and cleanup liabilities. Facilities are typically required to maintain spill prevention plans, implement secondary containment for tanks and drums, and follow OSHA and EPA regulations for labeling, storage, and handling of hazardous materials.

In addition to chemical hazards, gas turbines generate solid and liquid waste streams over their operational life. These include used oil and filters, chemical residues, wastewater from cooling or cleaning operations, and metallic waste from maintenance or component replacement. Some parts, such as turbine blades and liners, may be coated with high-performance alloys or ceramic materials that require specialized recycling or disposal procedures. Combined cycle plants also discharge blowdown water containing concentrated treatment chemicals, which must meet discharge permit limits or be treated on-site. To ensure compliance, operators must maintain detailed waste tracking logs, properly classify waste types, and work with certified disposal and recycling contractors. Effective waste management not only reduces environmental impact but also supports plant safety, regulatory compliance, and sustainability goals.

5 Site Feasibility

Proximity to Energy Resources & Infrastructure

Large Natural gas generators can be located anywhere there is access to a sufficient natural gas pipeline, water resource, and electrical transmission.  Maps of natural gas pipelines in the US can be found at the National Pipeline Mapping System [19].  The size of the pipeline needed depends on the size of the power plant and other customers on the pipeline.  While pipeline size depends on several factors, Table 5.3 shows a representative minimum pipeline size to support different natural gas power plant sizes.

Table 5.3.  Minimum Pipeline size required to support a Natural Gas Power Plant.
Power Plant Capacity (MW) Estimated Pipeline Diameter (inches) Notes
10 6–8 Small industrial or backup facility
50 8–12 Small plant or distributed energy
100 14–16 Mid-size simple-cycle gas turbine
500 24–30 Mid-size combined cycle
1,000 36+ Very large, utility-scale facility

Land Use & Power Density

Land requirements for gas electric power consists of space needed for the gas delivery system, the gas turbine and generator, the HRSG, the steam turbine and generator, the substation, auxiliary systems, access roads, maintenance clearances, control buildings, and safety buffers.  Simple cycle systems are more compact due to fewer components, achieving a power density of approximately 14–25 MW per acre. Combined cycle systems, with their additional HRSGs and steam turbines, have a lower power density of 10–17 MW per acre.

Natural gas generators primarily use pipeline-supplied fuel, minimizing the need for on-site storage. Still, backup storage using LNG or CNG may be desirable. To support 24–48 hours of operation, systems require approximately 100–200 gallons of LNG per MW, depending on efficiency (simple cycle: ~10,000,000 BTU/MWh; combined cycle: ~6,500,000 BTU/MWh). A 20,000-gallon LNG tank with spill containment and regulatory setbacks, typically requires 800–1,200 sq ft, plus extra space for vaporizers and piping. A total storage area of 2,000–3,000 sq ft (0.05–0.07 acres) is generally adequate with pipeline access and a single tank. [18] [19]

Aesthetics and Acoustic Considerations

Steam emitted from a stack blocks views
Figure 5.3. Steam visible from natural gas emissions stack. Credit: Authors created using ChatGPT.

Natural gas power plants and their infrastructure, such as pipelines and transmission lines, alter the visual landscape, particularly in undeveloped areas. Natural gas power plants typically have turbine units at a height of 100 feet with stacks up to 200 feet high.  Steam clouds associated with the cooling system can tower above the plant for hundreds of feet into the air.  Above-ground transmission lines on large towers are common, and vegetation clearing for pipelines or access roads can disrupt scenic views and habitats. Underground lines are less visually intrusive but costlier and less common outside urban areas. [22]

The noise levels of SCGTs and CCGTs vary based on design and mitigation measures. SCGTs typically produce 85–95 dB at 23 feet, with aeroderivative models potentially achieving 75–85 dB with noise suppression, due to their high-speed operation and exhaust systems. CCGTs, benefiting from stable operation and heat recovery systems, generate 80–90 dB, reducible to 70–80 dB with advanced enclosures. [23]

Public Perception & Perceived Harm

Both simple and combined natural gas generator systems raise concerns about air quality degradation, particularly in urban areas, and their reliance on fossil fuels perpetuates climate change risks. Additionally, community-level impacts include noise pollution and land use conflicts.

6 Evolving Policy

Policy Volatility

As the demand for cleaner energy intensifies, understanding the regulatory landscape governing natural gas turbine projects is essential for developers, policymakers, and environmental stakeholders. The Clean Air Act (CAA) establishes a comprehensive regulatory framework for utility-scale natural gas turbine projects, including both simple and combined cycle systems. Under Section 111, the EPA enforces New Source Performance Standards (NSPS) that set CO₂ emission limits based on turbine operational roles—800 lb./MWh-gross for base-load combined cycle units, 1,170 lb./MWh-gross for intermediate-load, and 160 lb./MMBtu for low-load turbines using low-emitting fuels. Although a 2032 mandate for carbon capture and storage (CCS) was previously proposed for base-load units, it has been delayed due to cost and feasibility concerns, though it may be revisited in future rulemaking. Additionally, turbines must comply with performance-based permitting and employ Best Available Control Technology (BACT), which typically includes SCR for NOₓ, oxidation catalysts for CO, and operational best practices. Projects emitting over 100 tons per year of any criteria pollutant must also obtain a Title V Operating Permit, requiring ongoing monitoring and reporting.

Looking forward, several policy changes could reshape the regulatory landscape. The EPA may tighten NSPS limits or reintroduce CCS requirements as technology improves or national climate goals evolve. BACT determinations could also expand to include more advanced emissions controls or consider lifecycle emissions and environmental justice factors. On the permitting side, federal and state reforms aimed at accelerating clean energy development may streamline Title V and PSD processes but could also introduce stricter environmental reviews or community engagement requirements. These potential changes add regulatory uncertainty that could affect project feasibility, costs, and deployment timelines—especially in regions with aggressive decarbonization targets or non-attainment air quality zones.

Incentives

Federal incentives have played a pivotal role in shaping the economics and design strategies of natural gas power plants, particularly regarding carbon capture integration. Under the Bipartisan Infrastructure Law and the Inflation Reduction Act (IRA), developers benefited from grants and funding to upgrade emission control systems and deploy lower-emission units. The IRA notably enhanced the Section 45Q tax credit, offering $85 per ton for geologic sequestration and $60 per ton for CO₂ utilization, significantly improving the financial viability of carbon capture projects. In late 2023, the Department of Energy awarded nearly $890 million for commercial-scale carbon capture demonstrations at natural gas combined-cycle plants, reinforcing federal commitment to decarbonizing the power sector. These incentives encouraged the design of “capture-ready” facilities and opened new pathways for CO₂ reuse in industrial applications such as synthetic fuel production and concrete curing. [24]

However, the landscape shifted in mid-2025 with the passage of the One Big Beautiful Bill Act, which introduced new restrictions and structural changes to clean energy tax credits. While the Section 45Q credit values were preserved—maintaining $85/ton for point-source capture and $180/ton for direct air capture—the bill imposed Foreign Entity of Concern (FEOC) rules that disqualify entities with ownership or supply chain ties to certain nations (e.g., China, Iran, Russia, North Korea) from claiming the credit. These restrictions complicate project financing and supply chain planning, especially for developers relying on global equipment sourcing. Additionally, while the credit remains inflation-adjusted starting in 2027, the broader clean energy sector saw accelerated phase-outs and eligibility tightening for other technologies. As a result, while carbon capture remains economically viable, the 2025 policy changes introduce greater regulatory complexity and geopolitical risk, prompting developers to reassess siting, partnerships, and long-term investment strategies for CCGT plants. [25] [26]

Other Policy Risks

While federal emissions regulations and incentives often dominate the conversation around natural gas power development, a broader array of policy risks can significantly affect project viability and design. Several agencies at the federal, state, and local levels have the authority to rapidly implement policies that can hinder or even block natural gas projects. For example, the EPA and state air agencies can revise emission limits or reporting requirements, potentially requiring costly retrofits or delaying permitting. State environmental bodies, such as the Texas Commission on Environmental Quality (TCEQ), may impose fuel usage restrictions or alter permitting frameworks, affecting fuel flexibility and operational planning. Additionally, local utility commissions and public utility commissions can influence project timelines and feasibility through certificate-of-need processes, interconnection reviews, or policy shifts that affect grid access and market participation.

Beyond regulatory agencies, market and geopolitical factors introduce further uncertainty. Natural gas prices are highly sensitive to international trade policies, domestic production levels, and seasonal demand, making long-term cost forecasting difficult. Sudden changes in LNG export regulations or pipeline capacity constraints can lead to unpredictable price spikes, undermining financial models. Local jurisdictions may also impose stricter emissions requirements than federal standards—California’s NOx limits, for instance, are enforced through regional air quality districts and can necessitate advanced control technologies. [27] Emerging climate policies targeting upstream methane emissions or introducing new rules for combustion-related pollutants like NOx and CO₂ add another layer of complexity. Together, these factors create a dynamic and often fragmented policy environment that developers must navigate carefully when planning and operating natural gas turbine facilities.

7 Cost of Capacity & Energy

While simple and combined cycle natural gas power plants offer relatively low upfront capital costs and fast dispatch capabilities, their long-term competitiveness can be challenged by fluctuating fuel prices and higher operating expenses—particularly when compared to geothermal or other low-operating-cost resources under specific market conditions.

Capital and Operational Expenditures

The major components of capital expenditure (CAPEX) for turnkey gas-fired power plants include turbine-generator packages, electrical interconnection equipment, and, for combined cycle configurations, heat recovery steam generators (HRSGs) and associated steam turbines. Fuel supply infrastructure and emissions control technologies, including selective catalytic reduction (SCR) systems or oxidation catalysts, are also commonly included depending on regulatory requirements. Based on industry benchmarks , turnkey installed costs range from $1,150,000 to $1,450,000 per MW for simple cycle gas turbines (SCGTs), and from $1,200,000 to $1,600,000 per MW for combined cycle gas turbines (CCGTs). [28]

Fixed OPEX typically ranges from $4 to $12 per MWh, depending on plant size, age, and configuration. Variable costs include wear-based maintenance, emissions treatment, and fuel. Variable O&M, not including fuel, averages $3 to $5 per MWh for both SCGTs and CCGTs. Fuel costs represent the largest share of OPEX; with a delivered natural gas price averaging $5.75/MMBtu, and assuming heat rates of 8,000 to 10,000 Btu/kWh for SCGTs and 7,000 to 8,000 Btu/kWh for CCGTs, fuel costs range from $34 to $70 per MWh for SCGTs and $30 to $61 per MWh for CCGTs.  Water cost is generally minimal ([latex]~0.0028 $/MWh[/latex]) compared to the other costs considered.

Pipeline natural gas (PNG) generally ranges from $2.00 to $6.00 per Million Btu (MMBtu) at the hub.  Gas is susceptible to price spikes and has been as high as $16/MMBtu.  Figure 5.4 shows the volatility of gas prices over the past 27 years.  When sourced from alternative supply methods, such as liquefied natural gas (LNG) or compressed natural gas (CNG), fuel costs can vary significantly from pipeline-delivered prices. LNG prices are typically 2 to 5 times higher than PNG, while  CNG has a $3/MMBtu premium over PNG.  In rare cases, LNG and CNG may be cost-competitive with pipeline gas due to regional price differentials or surplus supply conditions, but they are more often associated with higher delivered fuel costs due to liquefaction, compression, and transportation expenses.

Historical Nat Gas Prices
Figure 5.4.  Henry Hub Natural Gas Spot Prices by month, $/Million Btu.  Credit: Chris Boyer using data from Reference [29].

 

Levelized Cost of Capacity and Levelized Cost of Energy

Based on the numbers above, the levelized cost of capacity (LCOC) for a SCGT plant ranges from $112,000 to $197,000 per MW per year, and a CCGT plant ranges from $116,000 to $224,000 per MW per year. SCGTs are often favored for peaking, backup, or standby applications due to their lower capital investment and faster ramp-up capabilities. The comparatively lower LCOC of SCGTs, particularly when operated intermittently, makes them more cost-effective in roles where high efficiency is less critical than quick response and minimal idle cost. While CCGTs can also be configured for flexible operations, their higher upfront and fixed costs reduce their attractiveness for such intermittent use unless higher capacity factors can be achieved.

Pie chart showing cost allocations of LCOE
Figure 5.5:  LCOE breakdown for Combined Cycle Gas Turbines.  Low-end cost, high utilization case.

The levelized cost of energy (LCOE) for natural gas generation varies significantly depending on configuration: SCGTs range from $49/MWh with low-end costs and high utilization to $257/MWh for peaker operation with high-end cost, while CCGTs range from $38/MWh to $109/MWh. While the utilization (capacity factor) is important, the primary driver of LCOE is fuel cost, which constitutes the largest share of ongoing operating expenses as shown in Figure 5.5 and Figure 5.6. SCGTs are particularly sensitive to fuel prices due to their lower thermal efficiency and higher heat rates, whereas CCGTs offer better fuel economy through improved efficiency and energy recovery via steam cycles as shown in Table 5.4 and Table 5.5. This makes CCGTs the more favorable option for baseload or intermediate-duty operation where sustained fuel savings can offset higher capital costs.

Despite the fuel cost sensitivity, natural gas remains a formidable choice for power generation particularly for dispatchable capacity. Unlike intermittent renewable sources, gas turbines can deliver power on demand, which is critical for grid reliability and peaking demand. When accounting for the value of firm, on-call power delivery, the LCOE of gas, especially for CCGTs, becomes competitive even when compared to lower-cost renewables, because it ensures consistent system stability without the need for extensive storage or backup systems.

LCOE decreases with utilization and fuel cost
Figure 5.6: LCOE versus utilization at different Fuel Costs for the Combined Cycle Gas Turbine facility.

 

Table 5.4:  Simple Cycle Gas Turbines Cost Parameters used for the LCOC & LCOE Calculations
Unit Base Low Base High Base Average
CAPEX $/MW $1,150,000 $1,450,000 $1,300,000
OPEX Fixed $/MW/yr $10,000 $17,000 $13,500
OPEX Variable $/MWh $3.50 $5.00 $4.25
Incentive %CAP Red
Life Yrs 30 30 30
Discount Rate % 8% 12% 10%
Capacity Factor % 82% 13% (Peaker) 61%
Fuel + Delivery Cost $/MMBtu $2.75 $5.75 $4.25
Fuel Rate MBtu/MWh 10900 12550 11725
LCOC $/MW/yr $112,000 $197,00 $151,00
LCOE CAPEX $/MWh $14.25 $164.39 $25.86
LCOE OPEX $/MWh $4.90 $20.53 $6.79
LCOE FUEL $/MWh $29.98 $72.16 $49.83
LCOE Total $/MWh $49.13 $257.08 $82.48
Table 5.5: Combined Cycle Gas Turbines Cost Parameters used for the LCOC & LCOE Calculations
Unit Base Low Base High Base Average
CAPEX $/MW $1,200,000 $1,600,000 $1,400,000
OPEX Fixed $/MW/yr $10,000 $25,500 $17,750
OPEX Variable $/MWh $2.75 $5.00 $3.88
Life Yrs 30 30 30
Discount Rate % 8% 12% 10%
Capacity Factor % 82% 42% 61%
Fuel + Delivery Cost $/MMBtu $2.75 $5.75 $4.25
Fuel Rate MBtu/MWh 6950 7475 7213
LCOC $/MW/yr $116,600 $224,000 $166,000
LCOE CAPEX $/MWh $14.87 $54.42 $27.85
LCOE OPEX $/MWh $4.15 $11.99 $7.20
LCOE FUEL $/MWh $19.11 $42.98 $30.65
LCOE Total $/MWh $38.13 $109.39 $65.71

References

[1] K. Clark, "Long lead times are dooming some proposed gas plant projects", Power Engineering, February 20, 2025, [Online] Available: https://www.power-eng.com/gas/turbines/long-lead-times-are-dooming-some-proposed-gas-plant-projects/ [Accessed 26 Aug 2025].

[2] Alberta Energy Regulator (formerly ERCB), "Directive 077: Pipelines – Requirements and Reference Tools," Alberta Energy Regulator, 15 November 2023. [Online]. Available: https://www.aer.ca/documents/directives/Directive077.pdf. [Accessed 19 June 2025].

[3] K. Clark, "Long lead times are dooming some proposed gas plant projects," Power Engineering, 20 February 2025. [Online]. Available: https://www.power-eng.com/gas/turbines/long-lead-times-are-dooming-some-proposed-gas-plant-projects/. [Accessed 21 July 2015].

[4] Power‑Technology, "Cascade Combined-Cycle Gas Turbine Power Plant, Alberta, Canada," Power‑Technology, 8 December 2023. [Online]. Available: https://www.power-technology.com/projects/cascade-combined-cycle-gas-turbine-ccgt-power-plant-alberta/. [Accessed 13 June 2025].

[5] Power System Dynamic Performance Committee, "Dynamic Models for Turbine‑Governors in Power System Studies," IEEE Power & Energy Society, 29 January 2013. [Online]. Available: http://sites.ieee.org/fw-pes/files/2013/01/PES_TR1.pdf. [Accessed 13 June 2025].

[6] P. Decoussemaeker, A. Nagasayanam, W. Bauver, L. Rigoni, L. Cinquegrani, G. Epis and M.-E. Dought, "Startup Time Reduction for Combined Cycle Power Plants," GE Power, Brussels, 2016.

[7] M. Joshi and S. Rehman, "Ramping Up the Ramping Capability: India’s Power System Transition," National Renewable Energy Laboratory (NREL), September 2020. [Online]. Available: https://docs.nrel.gov/docs/fy20osti/77639.pdf. [Accessed 11 June 2025].

[8] IEEE Power System Relaying & Control Committee, "Practices for Generator Synchronizing Systems (IEEE PES PSRC Report No. 119)," IEEE Power & Energy Society, April 2024. [Online]. Available: https://www.pes-psrc.org/kb/report/119.pdf. [Accessed 11 June 2025].

[9] Office of Air and Radiation, "Efficient Generation: Combustion Turbine Electric Generating Units," U.S. Environmental Protection Agency (EPA), May 2023. [Online]. Available: https://www.epa.gov/system/files/documents/2023-05/TSD%20-%20Efficient%20Generation%20Combustion%20Turbine.pdf. [Accessed 11 June 2025].

[10] Claire Soares, "Gas Turbines in Simple Cycle Mode: Introduction (Section 1.1)," in Gas Turbine Handbook – NETL’s handbook, Morgantown, WV, U.S. DOE – National Energy Technology Laboratory, 2006, p. 74.

[11] U.S. Environmental Protection Agency, "EPA (2024) Inventory of U.S. Greenhouse Gas Emissions and Sinks: 1990-2022. EPA 430-R-24-004," 15 April 2024. [Online]. Available: https://www.epa.gov/ghgemissions/inventory-us-greenhouse-gas-emissions-and-sinks-1990-2022. [Accessed 21 July 2025].

[12] K. Clark, U.S. making water efficiency gains in power sector, Power Engineering, June 14,2023. [online] https://www.power-eng.com/operations-maintenance/u-s-making-water-efficiency-gains-in-power-sector/.  [Accessed 26 Aug 2025].

[13] J. Macknick, R. Newmark, G. Heath, and K. Hallett, "A Review of Operational Water Consumption and Withdrawal Factors for Electricity Generating Technologies", National Renewable Energy Laboratory, Technical Report NREL/TP-6A20-50900, March 2011.

[14] M. Harris and T. Diehl, "Withdrawal and Consumption of Water by Thermoelectric Power Plants in the United States, 2015", U.S. Geological Survey Water Availability and Use Science Program, Scientific Investigations Report 2019–5103,  [online] https://doi.org/10.3133/sir20195103

[15] U.S. Energy Information Administration, "Natural Gas and the Environment," U.S. Energy Information Administration, 16 April 2024. [Online]. Available: https://www.eia.gov/energyexplained/natural-gas/natural-gas-and-the-environment.php. [Accessed 21 May 2025].

[16] Global Energy Monitor (GEM), "Fracking and water consumption," 30 April 2021. [Online]. Available: https://www.gem.wiki/Fracking_and_water_consumption. [Accessed 23 July 2025].

[17] U.S. Energy Information Administration, "Assumptions to the Annual Energy Outlook 2025: Electricity Market Module," U.S. Energy Information Administration, March 2022. [Online]. Available: https://www.eia.gov/outlooks/aeo/assumptions/pdf/electricity.pdf. [Accessed 11 June 2025].

[18] U.S. Environmental Protection Agency, "Coal Plant Decommissioning, Remediation and Redevelopment," U.S. Environmental Protection Agency, June 2016. [Online]. Available: https://www.epa.gov/sites/default/files/2016-06/documents/4783_plant_decommissioning_remediation_and_redevelopment_508.pdf. [Accessed 11 June 2025].

[19] Pipeline and Hazardous Materials Safety Administration, "National Pipeline Mapping System," US Department of Transportation, 2025. [Online]. Available: https://www.npms.phmsa.dot.gov/. [Accessed 23 July 2025].

[20] W. Stiles, "Defining NFPA 37," Consulting & Specifying Engineer, 16 December 2015. [Online]. Available: https://www.csemag.com/defining-nfpa-37/. [Accessed 13 June 2025].

[21] Curtis Power Solutions, "NFPA 110 Installation and Environmental Considerations," Curtis Power Solutions, 2025. [Online]. Available: https://www.curtispowersolutions.com/nfpa-110-installation. [Accessed 13 June 2025].

[22] U.S. Energy Information Administration, "Electricity Expplained: Electricity and the Environment," U.S. Energy Information Administration, 16 April 2024. [Online]. Available: https://www.eia.gov/energyexplained/electricity/electricity-and-the-environment.php. [Accessed 22 May 2025].

[23] B. Cazzolato, O. Leav and C.  Howard, "Environmental Noise from Open‑Cycle Gas Turbines," University of Adelaide, 27 April 2023. [Online]. Available: https://www.researchgate.net/publication/370299657_Environmental_Noise_from_Open-Cycle_Gas_Turbines. [Accessed 11 June 2025].

[24] International Energy Agency, "Inflation Reduction Act 2022: Sec. 13104 Extension and Modification of Credit for Carbon Oxide Sequestration," International Energy Agency Policies Database, 17 November 2022. [Online]. Available: https://www.iea.org/policies/16255-inflation-reduction-act-2022-sec-13104-extension-and-modification-of-credit-for-carbon-oxide-sequestration. [Accessed 8 June 2025].

[25] 119th Congress of The United States of America, "H.R.1 - One Big Beautiful Bill Act," congress.gov, 4 July 2025. [Online]. Available: https://www.congress.gov/bill/119th-congress/house-bill/1. [Accessed 6 August 2025].

[26] Global CCS Institute, "U.S. Preserves and Increases 45Q Credit in “One Big Beautiful Bill Act”," Global CCS Institute, 8 July 2025. [Online]. Available: https://www.globalccsinstitute.com/news-media/latest-news/u-s-preserves-and-increases-45q-credit-in-one-big-beautiful-bill-act/. [Accessed 6 August 2025].

[27] Ventura County Air Pollution Control District, "Final Staff Report: Proposed Amendments to Rule 74.23, Stationary Gas Turbines," Ventura County Air Pollution Control District, November 2019. [Online]. Available: https://ww2.arb.ca.gov/sites/default/files/classic/technology-clearinghouse/rules/RuleID4547sr.pdf. [Accessed 12 June 2025].

[28] LAZARD , "Levelized Cost of Energy + June 2025," LAZARD Inc., 16 June 2025. [Online]. Available: https://www.lazard.com/media/eijnqja3/lazards-lcoeplus-june-2025.pdf. [Accessed 20 June 2025].

[29] U.S. Energy Information Administration, "Natural Gas," 6 Aug 2025. [Online]. Available: https://www.eia.gov/dnav/ng/hist/rngwhhdm.htm. [Accessed 7 Aug 2025].