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5 June 2025

23 Pages

Characterising Non-Intentional Supraharmonic Emissions from Inverters in Power Grids: Review and Challenges

,
and
Australian Power Quality Research Centre, University of Wollongong, Wollongong 2522, Australia
*
Author to whom correspondence should be addressed.
This article belongs to the Special Issue Advances in Power Converters and Inverters

Abstract

Supraharmonic emissions, referred to as voltage/current waveform distortions in the 2–150 kHz range, have been identified as an emerging power quality concern. With the increased number of non-linear devices connected to the power grid, such as photovoltaic inverter systems, supraharmonic disturbances are expected to increase. Despite being a source of supraharmonic emissions, power electronic equipment has become a ubiquitous technology due to recent advancements. Similarly, researchers around the world have started studying these emissions; however, complete systematic knowledge concerning supraharmonic emissions is yet to be achieved. This paper uniquely delves into characterising emissions using existing knowledge, significantly improving the understanding of their complex micro-level interactions and highlighting emerging challenges. The paper presents a comprehensive summary integrating existing studies on supraharmonic emissions in five key areas: emissions, propagation and attenuation, measurement techniques, modelling and simulation, and mitigation.

1. Introduction

Conventional power quality (PQ) studies have concentrated on voltage and current waveform distortions in the frequency range of 0–2 kHz; however, special attention has been paid to conducted emissions above 2 kHz over the past decade [1]. Waveform distortions in the 2–150 kHz frequency range are referred to as ‘supraharmonic emissions’ or ‘high-frequency harmonic emissions’; these emissions are categorised as intentional or non-intentional emissions [2]. Intentional emissions originate from any device or system designed to operate within the supraharmonic frequency range, where they are a planned and necessary part of its functionality (e.g., power line communication; PLC) that involves superimposing a high-frequency voltage signal onto a fundamental frequency voltage for communication purposes. Non-intentional emissions are generated as an unintended consequence of the operation, and mainly originate from power electronic (PE) devices due to their non-linear voltage–current characteristics [3]. Although PE interfaces are identified as a source of superharmonic, they have become a ubiquitous technology in almost every industry due to their high efficiency and flexibility. PE interfaces play a critical role in the energy industry, converting, controlling and conditioning electrical energy in an efficient way [4].
Distributed energy resources (DERs) are being connected to the grid in increasing numbers, and this trend is predicted to continue over the coming years, supporting the net-zero energy transition [5]. Regardless of the DER connection voltage level, every solar photovoltaic (PV) and wind renewable energy integration system equipped with a PE interface between the renewable energy source (RES) and the electricity supply network that is capable of introducing supraharmonic emissions in low-, medium- and high-voltage networks [6,7,8]. Figure 1 depicts the total renewable energy capacities and additions of different RES technologies in 2023. Among all technologies developed to achieve renewable energy targets, solar PV and wind are the most promising energy integration systems. In 2023 alone, solar PV and wind power capacity additions have increased by 34% and 13%, respectively. This is equivalent to 524 GW out of 536 GW of the total renewable energy additions in the year 2023. Other renewable power corresponds to geothermal power and heat, bioenergy and solar thermal heating.
Figure 1. Installed capacities of renewable energy sources by technology [5].
Based on the signal type, in either time or frequency domains, supraharmonic emissions fall under three categories, namely, narrowband, broadband and recurrent oscillations [9,10]. Despite recurrent oscillations in the time domain, whether the emission is narrowband or broadband is determined based on the concentration of spectral components in the frequency domain. This frequency spectrum relies on parameters such as the signal measurement window, signal analysis window, and grouping method of frequency components, i.e., a 200 Hz grouping method might show a broadband signal while the 2 kHz grouping method shows a narrowband signal for a particular time domain signal. Electromagnetic compatibility (EMC) filters amplify the recurrent oscillations, and the same signal can be identified as either narrowband or broadband in the frequency domain [9]. The classification of supraharmonic emissions is depicted in Figure 2 with each signal type identified as follows:
Figure 2. Classification of supraharmonic emissions.
  • Narrowband signals: identified as individual frequencies in the frequency domain, mainly due to PLC.
  • Broadband signals: identified as a spectrum of adjacent frequency components in the frequency domain, mainly due to individual end-user equipment with active power-factor correction (APFC).
  • Recurrent oscillations: typically identified in every 10 ms in the time domain, mainly due to PE converters around the current zero-crossing.
Several PQ issues have been reported due to supraharmonic emissions, including audible noise, cable termination failures, tripping of residual current devices, flicker, and the disruption of PLCs [11,12]. A key difficulty in managing supraharmonic emissions is the lack of normative measurement methods to enable characterisation and enable further analysis [13]. As such, a rigorous and standardised measurement technique is required for evaluating EMC levels at frequencies above 2 kHz. Figure 3 depicts a summary of existing regulations that define the measurement/summation techniques to be used for waveform distortion across various frequency ranges.
Figure 3. Existing regulations for measurement and summation techniques for waveform distortion across various frequency ranges [14,15].
Recently, researchers have devoted significant effort to developing systematic knowledge on supraharmonic emissions from equipment connected to electricity supply networks. Understanding the harmonic behaviour of multiple gird-tied inverters against the background voltage is studied in [16,17]. Appliances and equipment that have been evaluated include solar PV inverters [18,19,20,21], wind farms [22], LED lamps [23] and electric vehicle (EV) chargers [24]. Current waveforms of four supraharmonic sources—PV inverter (2.5 kW), EV, LED and televisions—were analysed in [25] to identify high-frequency emissions. The study emphasises that time-frequency (hybrid) analysis is important for fully understanding supraharmonic emissions in addition to time domain and frequency domain analysis. Supraharmonic reduction by spreading the spectrum of the emission in a randomised manner is discussed in [26]. Similarly, the authors of [27] investigated supraharmonic emissions from rolling mill converters and proposed a mitigation strategy under a random carrier frequency PWM method.
Through a comprehensive examination of diverse methodologies presented by researchers around the world, readers are able to identify existing power quality challenges in power grids. Existing review papers have made valuable contributions for understanding this supraharmonic emission phenomenon, including those on supraharmonic emission sources [28,29,30,31], measurement methods and standards [28,29,30,32,33,34], effects [29,30,33], mitigation techniques [29,31,33], and modelling and simulation [30]. Significant attention is paid to intentional and non-intentional sources, measurement and potential mitigation. However, only limited attention is paid to analysis and characterisation. Developing a comprehensive overview of the field of supraharmonic emissions related to inverters is limited, with existing papers covering all areas. This review offers a timely and critical synthesis of the literature on supraharmonic emissions from inverters, specifically highlighting the emerging challenges and opportunities in five key areas: emissions, propagation and attenuation, measurement techniques, modelling and simulation, and mitigation. While previous systematic reviews have focused on providing general overviews, this review uniquely delves into characterising these emissions using advanced methods, such as phase angle representation, and improving understanding of the complex interactions that occur at the micro-level.
The authors’ other research identifying and characterising different types of supraharmonic phenomena associated with solar PV inverters is presented, addressing some of the challenges identified in this study. Section 2 provides an overview of supraharmonic emissions associated with PE interfaces of RESs. Supraharmonic propagation and attenuation characteristics are discussed in Section 3. Section 4 covers the three existing measurement techniques defined by standardisation bodies, identifying alternative measurement techniques in the literature. Section 5 provides an overview of supraharmonic modelling and simulation approaches used in supraharmonic analysis. Mitigation techniques are provided in Section 6. Section 7 provides a summary of supraharmonic emissions associated with PE converters.

2. Emissions

The sources of high-frequency emissions are not restricted to RESs. Any device with a PE interface, such as street lamps, emits non-intentional emissions with different devices exhibiting different frequency spectra. A list of supraharmonic sources and general high-frequency ranges is provided in [6] as follows:
  • Industrial size converters (9–150 kHz)
  • Street lamps (up to 20 kHz)
  • EV chargers (15–100 kHz)
  • PV inverters (4–20 kHz)
  • Household devices (2–150 kHz)
  • PLC (9–95 kHz)

2.1. Switching Frequency Emissions

Switching frequency emissions are a predominant type of supraharmonic emission phenomenon, generated by the high-frequency switching of PE devices. These emissions are intrinsic to the operation of devices like voltage source converters (VSCs) and pulse-width modulated (PWM) converters.
The voltage/current waveforms at the output of a PE converter consist of supraharmonic emissions, the primary emission of which has been studied extensively [25,35,36]. The frequency spectrum of the voltage produced by PV inverters is dependent on several factors, including the frequency modulation index, the PWM switching technique (unipolar or bipolar), the use of multi-level PWM, three-phase or single-phase design, the amplitude modulation index, phase shifting, and dead zones [36,37]. Thus, the output voltage of a PV inverter is generally not periodic and does not follow a simple Fourier series. However, the harmonic spectrum of these waveforms follows the first type of Bessel function and can be written as (1) [38,39].
V i n v ( t ) = M V d c 2 s i n ( ω t ) + 2 V d c π ∑ m = 1 , 3 , . . + ∞ ∑ n = 0 , ± 2 , ± 4 , . . ± ∞ 4 J n ( m M π / 2 ) 3 m s i n ( m π 2 ) s i n 2 ( n π 3 ) c o s ( m ω s w t + n ω t ) + 2 V d c π ∑ m = 2 , 4 , . . + ∞ ∑ ± 1 , ± 3 , . . ± ∞ 4 J n ( m M π / 2 ) 3 m c o s ( m π 2 ) s i n 2 ( n π 3 ) s i n ( m ω s w t + n ω t ) ,
where M is the modulation index (amplitude ratio between the modulation wave and the carrier wave), V i n v is the inverter output terminal voltage, V d c is the DC link voltage, ω s w is the switching frequency, and J n is the first type of Bessel function. M is crucial for employing PWM techniques, which are used to mitigate EMI by distributing the emission energy over a wider frequency range and thus lowering the peak emission levels at specific frequencies [40].
The existing work in the literature on supraharmonic emission caused by high-frequency switching is summarised in Table 1.
Table 1. Existing work on characterising PWM-based spectral components.

2.2. Challenges

Some of the challenges identified in the reviewed literature in relation to understanding supraharmonic emissions are as follows:
  • Understanding other types of emission phenomena associated with PE converters in addition to switching frequency emissions.
  • Generalisation of supraharmonic characteristics for similar types of devices, different types of devices, and interactions between neighbouring PE converters.
  • Is it acceptable/sufficiently accurate to focus only on primary emissions (disregarding secondary emissions) for high-frequency emissions studies? If so, is it valid for the full range (2–150 kHz) or any specific frequency range depending on the emission characteristics?
  • Development of systematic knowledge on diversity between the emission spectra from individual devices, diversity in the time of use of equipment, and cancellation of emission in the complex plane.

3. Propagation and Attenuation

Several studies have been performed to understand supraharmonic propagation in low-voltage (LV) networks. A generalised expression for the voltage at a particular frequency is provided in [30], which can be used for propagation studies of supraharmonic emissions. The voltage at frequency f at a bus r is expressed in (2), where Z r s ( f ) is the transfer impedance from bus s to bus r and I s ( f ) is the current flowing to bus s. All parameters in this expression are complex numbers and rapidly changing with time. The transfer impedance between neighbouring devices is influenced by the number of devices and variable load conditions.
U r ( f ) = ∑ s = 1 N Z r s ( f ) · I s ( f ) .
This expression does not address non-linear phenomena, and there is no definitive knowledge on how these will impact propagation in the superharmonic range.

3.1. Primary and Secondary Emission

To understand supraharmonic emissions and their propagation characteristics within and from installation, two driving forces are identified, termed “primary emission” and “secondary emission” [34]. Primary emission is the part of the supraharmonic emission at the device terminals driven by the sources within the device (driven by current), whereas secondary emission is the part of the supraharmonic emission driven by the sources outside of the device (driven by voltage). The authors of [30] have provided a simplified network model used to represent these emissions as depicted in Figure 4, where:
Figure 4. Simplified network model to understand supraharmonic emissions.
  • I represents the total supraharmonic emission.
  • I N and Z N represent the Norton equivalent of internal emission and impedance, respectively.
  • E g and Z g represent the Thevenin equivalent of background voltage and grid impedance, respectively.
Expressions for primary and secondary emissions are derived and represented in (3) and (4). The differentiation of these two forces from field measurements where both primary emissions and secondary emissions are present is not a simple task [6]. The combination of both primary and secondary emissions is yet to be completely distinguished.
I 1 = Z N Z N + Z g · I N ,
I 2 = 1 Z N + Z g · E g .

3.2. Propagation Between Devices Within Installation

The propagation between devices within an installation is directly influenced by the impedance seen by the supraharmonic source and the devices within the installation. The work presented in [45] concludes that when the number of devices with supraharmonic emissions increases within an installation, the total supraharmonic emissions flowing into the electricity network decrease. In general, supraharmonic emissions tend to flow within devices rather than propagate to the grid, and the number of supraharmonic emitting devices connected within the installation changes emission characteristics [46,47].
The study presented in [48] concludes that line impedance is a significant influence factor on supraharmonic propagation in industrial networks where most of the supraharmonic currents tend to flow within the installation. Particularly, propagation of supraharmonic emissions by wind power plant is presented in [8]. However, the work presented in [49,50] shows that RES can be identified as dominating supraharmonic sources in MV and LV networks as their emissions propagate over a distance of several kilometres in electrical networks.
A simple model to investigate the supraharmonic emissions of an installation with N number of devices is provided in [10]. The total emission is inversely proportional to the square root of the number of devices. It is suggested that the emissions partially cancel each other out due to the phase angle diversity of individual supraharmonics. However, some studies indicate that this is due to the low impedance path within the installation introduced by EMC filters. The authors of [49] propose a method to determine the partial contributions of supraharmonic emissions to the common supraharmonic distortion at a node; however, the study does not consider the non-linear transfer characteristics of the instrumentation transformer used to measure supraharmonic emissions in the MV network.

3.3. Propagation in an LV Network

The authors of [51] have examined the propagation of supraharmonic emissions in an LV network using a cascade of two-port network representation, which is shown in Figure 5. The main advantage of the two-port model is that the derivation of ABCD parameters can be obtained with a limited number of measurements.
Figure 5. Two-port network representation.
  • V s and I s represent sending end voltage and current, respectively.
  • V r and I r represent receiving end voltage and current, respectively.
  • Z and Y represent impedance and admittance, respectively.
V s I s = A B C D V r I r
where,
A= 1 + Y Z / 2
B= Z
C= Y ( 1 + Y Z / 4 )
D= 1 + Y Z / 2
The existing work in the literature that aims to understand supraharmonic propagation is summarised in Table 2.
Table 2. Existing work on supraharmonic propagation.

3.4. Challenges

Some of the challenges identified in relation to understanding supraharmonic propagation and attenuation are as follows:
  • How can the difference between primary and secondary emissions be distinguished in high-frequency emission studies?
  • What is the explanation for two different harmonic spectra observed in the current measurement at the terminal of an individual device and the summated current? Is it due to emission characteristics or a low impedance path created by the front-end filters of devices? Is this identified throughout the complete high-frequency range (2–150 kHz)?
  • The accuracy of the two-port network model needs to be assessed in a more simplified way by measuring supraharmonic emissions at both ends of a radial cable.
  • Accurate measurement of supraharmonic emissions in MV/HV networks to quantify the propagation where direct measurement options are unavailable.

4. Measurement/ Summation Techniques

The three methods stipulated in international regulations, i.e., IEC 61000-4-7 [56], IEC 61000-4-30 [57] and CISPR 16-1-1 [58], are based on frequency domain analysis. As per the Nyquist criterion, the maximum frequency of the frequency-domain ( f m a x ) shall be half of the sampling frequency ( f s ) used to measure the time-domain waveform [59]. The time-domain signal and the frequency spectrum after the discrete Fourier transformation (DFT) are illustrated in Figure 6. Despite the involvement of DFT in all three methods, there are a few differences in their measurement and analysis intervals [60]. The measurement interval is the time period across which the DFT is applied. The analysis interval is the minimum time window in which a measurement result must be produced in accordance with the international regulation. Table 3 provides a comparison of measurement and analysis intervals for the three measurement methods. A graphical representation of Table 3 is depicted in Figure 7.
Figure 6. Relationship between time domain waveform and frequency spectrum after the DFT (a) time domain signal (b) frequency spectrum.
Table 3. Comparison of measurement and analysis intervals defined in the three methods.
Figure 7. Measurement intervals for a 200 ms analysis interval: (a) time-domain signal, (b) IEC 61000-4-7, (c) IEC 61000-4-30, (d) CISPR 16-1-1.

4.1. IEC 61000-4-7

IEC 61000-4-7 is a standard that provides guidelines for measuring harmonic and interharmonic distortion in AC power systems. The standard differentiates between harmonics and interharmonics and considers measurements of components up to 9 kHz (above harmonic frequencies) using DFT.
Annex B (informative) of IEC 61000-4-7 defines the employment of a frequency analysis technique with a frequency resolution of 5 Hz and a 200 Hz band aggregation using 200 ms of signal to measure harmonic emissions up to 9 kHz. The method involves grouping spectral components according to the root sum squared (RSS) method with possible aggregations in time. It is well-established, widely used in power quality analyses, and provides detailed frequency and magnitude information for supraharmonic components.
One of the advantages of the IEC 61000-4-7 measurement methodology is that it is gapless and has a very good reproducibility. However, power system disturbances vary over time, and continuous measurement of the entire frequency range is essential for accurate assessment. Due to the fixed longer measurement interval (200 ms), this methodology may be less suitable for determining the characteristics of supraharmonic signals, which vary rapidly in frequency or magnitude. The method is also susceptible to spectral leakage and windowing effects, which impact the accuracy of measurements.

4.2. IEC 61000-4-30

IEC 61000-4-30 provides guidelines for the measurement of power quality parameters in AC power supply systems. The measurement methodology defined in IEC 61000-4-30 is specifically focused on the measurement of voltage, current, and power quality parameters, including harmonics and interharmonics, in the frequency range up to 9 kHz and supraharmonics in the frequency range from 9 kHz to 150 kHz. Annex B (informative) specifies the use of DFT with 0.5 ms intervals, 2 kHz frequency resolution, and aggregation into average and maximum values of the 32 measurement intervals present in every 10/12 cycles for measuring supraharmonics emissions. This method is designed to provide detailed frequency and magnitude information for supraharmonic components in the specified frequency range.
One of the key advantages of the IEC 61000-4-30 methodology is the focus on the measurement of supraharmonics in the higher frequency range, which is increasingly relevant due to the proliferation of modern electronic equipment that is a source of emissions in this frequency band. The method provides a standardised approach for assessing supraharmonic distortion in power systems.
However, the IEC 61000-4-30 methodology may have limitations in accurately estimating supraharmonic components with low magnitudes and in the presence of noise. The measurement interval is 8% of the total analysis interval, causing it to disregard the majority of the measured data. The methodology may also exhibit reduced robustness to noise and limitations in performance when compared to alternative measurement methodologies, particularly in the presence of time-varying signals.

4.3. CISPR 16

CISPR 16 is a standard used for the assessment of emissions from equipment under test (EUT) in laboratory conditions, particularly for EMC testing. The measurement methodology involves the use of a spectrum analyser with a tuneable filter and detector (peak and quasi-peak) to measure emissions in the frequency range 9 kHz to 30 MHz. As specified in the standard, a digital quasi-peak detector is used to create an RC circuit analogue behaviour and a critically damped meter.
Measurement and analysis intervals for a Gaussian window ( α = 5.8) are used to ensure a −6 dB bandwidth of 200 Hz in [60]. Figure 7d depicts the same Gaussian window in which measurement interval is set as 20 ms with a 90% overlap. The schematic of the CISPR 16 measurement methodology is depicted in Figure 8.
Figure 8. Schematic of measurement method defined in the CISPR-16 standard.
Key aspects of the CISPR 16 method include:
1.
Laboratory setting: the methodology is primarily intended for use in a controlled laboratory environment for assessing emissions from individual EUT.
2.
Spectrum analyser: the methodology involves the use of a spectrum analyser equipped with a tuneable filter and detector to scan the frequency range sequentially over long measurement times.
3.
Peak and quasi-peak detection: the methodology utilises peak and quasi-peak detectors to assess emissions and their impact on radio transmission interference.
4.
Line impedance stabilisation network (LISN): the method may involve the use of an LISN to stabilise the line impedance in EMC testing that helps to ensure accurate and repeatable measurements of emissions from electronic devices [61,62].
Limitations and considerations associated with the CISPR 16 methodology, when considering application for electricity supply network measurements, include:
1.
Computational burden: implementing a digital instrument with the capability to measure the entire frequency range simultaneously may result in a high computational burden, particularly for evaluating the signal amplitude in each frequency band [13].
2.
Reproducibility: the tolerances of the methodology and the potential for different compliant implementations may raise concerns about the reproducibility of results, particularly for electricity supply network measurements [63].
3.
Relevance to power supply quality: while the methodology is useful for assessing emissions and their impact on radio transmission, questions have arisen regarding its relevance to assessing the quality of power supply in the electricity supply grid environments [64].

4.4. Alternative Methods

All three measurement methods mentioned in international regulations are considered non-parametric methods which involve DFT. However, attention has been drawn to parametric methods despite the higher computational burden requirement compared to non-parametric methods [65]. Alternative measurement methodologies have been developed and compared using synthetic signals or recorded power system waveforms in [60,66]. The authors of [67] proposed a method based on DFT analysis using a flat-top window, where the sliding measurement window is synchronised with the short-term fundamental period to reduce spectral leakage in measuring supraharmonic emissions. Table 4 summarises the existing work in the literature that develops alternative measurement techniques. Each method offers a unique approach with its own set of advantages and disadvantages concerning frequency and time resolution, noise immunity, computational complexity, and suitability for different applications. However, ongoing research and development efforts are focused on creating more standardised and precise digital approaches to address the growing need for reliable quasi-peak measurements in the supraharmonic frequency range.
Table 4. Existing work on alternative measurement methodologies.

4.5. Challenges

Some of the challenges identified in the reviewed literature in relation to supraharmonic measurement are as follows:
  • Supraharmonic measurement requires high time resolution capability to capture high-frequency waveform distortion, which cannot be achieved with conventional measuring equipment. Therefore, a normative measurement technique is required for the design of measuring equipment, which in turn is the key to the recording and analysis of high-frequency emissions.
  • Existing measurement techniques presented in standards provide indicative magnitude values, i.e., minimum, maximum, quasi-peak, RSS, for a group of supraharmonic emissions. Is there any possibility of defining a phase angle representation for a harmonic emissions band, allowing the identification of supraharmonic summation characteristics?
  • Lack of reproducibility with IEC 61000-4-30/CISPR measurement techniques.
  • No convention to differentiate narrowband and broadband signals in the frequency domain. A broadband signal in the IEC 61000-4-7 method (200 Hz resolution) may be identified as a narrowband signal in the IEC 61000-4-30 method (2 kHz resolution).

5. Modelling and Simulation

The control structure of a VSC is not a new topic and has been studied extensively [76,77,78,79,80]. Several studies have been undertaken with the aim of improving the control strategies related to PV inverter modelling.
The existing work in the literature on modelling approaches and simulation techniques is summarised in Table 5.
Table 5. Existing work on modelling and simulation techniques.

Challenges

Some of the challenges identified within the reviewed literature in relation to modelling and simulation are as follows:
  • A complete understanding of emission characteristics is missing due to the lack of accurate harmonic models. Comprehensive models are only available from the inverter manufacturer. Thus, a generic simulation model is necessary for understanding supraharmonic characteristics.
  • Models have been developed for harmonic analysis in the low-frequency range. However, the validity of these models in the high-frequency range is yet to be verified.
  • For a multiple inverter system, it is assumed that each inverter operates at the same operating state. Thus, the linear summation is valid for low-frequency harmonic emissions. Do high-frequency emissions follow the same principle irrespective of the emission phenomena?

6. Mitigation

Due to the interferences caused by supraharmonic emissions, recent attention has focused on the provision of mitigation techniques. A number of studies have begun to develop mitigating techniques without compromising the operation of the equipment. Oversizing of the filter will increase the cost unnecessarily, and undersized filters will be ineffective. Ref. [4] provides three different methods of mitigation: (a) reduction of emissions (equipment or installation), (b) improvement of network performance or reduction of the transfer level in the network, (c) improvement of immunity (equipment or installation).
The most practical way of mitigating supraharmonic emissions is by placing harmonic filters between the equipment and the grid. The filters should be designed considering the spectral impedances, secondary emissions and the resonances [10]. The author of [93] provides the three major methodologies for limitation of harmonics, where suitability depends on the current and voltage involved, the nature of the load and the system parameters such as the short circuit level at the point of connection.
The existing work in the literature on supraharmonic mitigation techniques is summarised in Table 6.
Table 6. Existing work on supraharmonic mitigation techniques.

Challenges

Some of the challenges identified within the reviewed literature in relation to harmonic mitigation are as follows:
  • There are many PWM modulation techniques that have been developed to reduce switching frequency emissions in PE converters. However, a quantitative analysis of these reductions is yet to be performed.
  • Lack of simulation models of PE converters makes it difficult to:
    1.
    Quantify the reduction of switching frequency emissions against PWM modulation technique.
    2.
    Introduce effective PWM modulation techniques to suppress switching frequency emissions.

7. Conclusions

This paper provides a comprehensive literature review on supraharmonic emissions from PE converters, highlighting the challenges in developing systematic knowledge. Five key areas—emissions, propagation and attenuation, measuring techniques, modelling and simulation, and mitigation—were considered to summarise the existing knowledge. There are three measurement methods available in the standards; however, no normative method has been accepted for field measurements. Further, conventional measuring instruments are only capable of measuring low-order harmonics, with high-frequency measurements requiring a significant additional computational burden depending on the measurement technique adopted. Thus, it is evident that a measurement standardisation framework for the supraharmonic frequency range is a pivotal requirement for assessing these emissions. This enables further research on standardisation work on imposing compliance limits for emissions in the supraharmonic range. With the advancements of PE interfaces, higher switching frequencies have been achieved, which has resulted in shifting resonance frequencies above 2 kHz. More research is needed in this direction to develop systematic knowledge on these two phenomena, preferably with high-frequency modelling techniques.
Substantial challenges remain in accurately measuring, comprehensively understanding, and effectively mitigating these high-frequency disturbances. The non-stationary nature of supraharmonics, the lack of standardised measurement techniques and emission limits, and the complexities of their propagation in modern electrical networks all contribute to the difficulties in understanding supraharmonic emissions. Further research work is required to develop existing systematic knowledge.
The development of accurate harmonic models of PE converters is challenging due to modelling complexities. According to the literature, the lack of accurate models makes it challenging to understand PE harmonic emission characteristics and provide mitigation techniques ensuring the reliable and sustainable integration of solar PV systems into the power grid.
A summary of the authors’ research work is presented in Table 7, assisting in characterising supraharmonic emissions while addressing some of the challenges identified in former sections. The time domain measurements were analysed using the measurement methodology specified in IEC 61000-4-7, which was extended for emissions above 9 kHz to maintain consistency. The contributions include identifying different types of phenomena associated with solar PV inverters, understanding/characterising emission phenomena from an identical inverter system, proposing phase angle representation methods to understand the phase angle diversity of supraharmonic emissions, and proposing switching frequency emission mitigation techniques that introduce new directions for future research.
Table 7. The authors’ other research work on characterising supraharmonic emissions from PV inverters.

Author Contributions

Conceptualization, K.P.; methodology, K.P. and S.E.; original draft preparation, K.P.; review and editing, S.E. and D.R. All authors have read and agreed to the published version of the manuscript.

Funding

This research received external funding from the Australian Government via the Global Innovations Linkage (GIL) program grant number: GIL73697.

Data Availability Statement

Data are contained within the article.

Conflicts of Interest

The authors declare no conflicts of interest.

Abbreviations

The following abbreviations are used in this manuscript:
ACAlternating current
APFCActive power factor correction
DCDirect current
DERDistributed energy resource
DFTDiscrete Fourier transform
EMCElectromagnetic compatibility
EUTEquipment under test
EVElectric vehicle
GILGlobal innovations linkage
LVLow voltage
MVMedium voltage
PEPower electronic
PECPower electronic converter
PLCPower line communication
PLLPhase locked loop
PQPower quality
PVPhotovoltaic
PWMPulse-width modulation
RESRenewable energy source
RSSRoot sum squared
VSCVoltage source converter

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