Exhibit C: Impact of Man-Made Noise From Broadband Over Power Line Systems Operating at the FCC Part-15 Radiated Emissions Limits on Worldwide HF Communications

 

Author: Ed Hare, ARRL Laboratory Manager
Date:  8/12/2003

 

1.         Methodology:

 

1.1              ARRL used the HFWIN32 VOACAP_INVERSE_AREA software program[1] to predict communications-circuit reliability on 14 MHz and 5 MHz under the following conditions for various man-made noise levels:

 

 

1.2       The man-made noise levels chosen for this study are:

 

 

 

 

 

1.3       ARRL used several levels of ambient man-made noise levels in its calculations:

 

Noise level dBW/Hz at 3 MHz as entered into the VOACAP program[3]

Noise level measured or extrapolated to 14 MHz

Environment

-153 dBW/Hz

-170.0 dBW/Hz

Best case measurements made by ARRL in a typical residential environment on quiet frequencies with minimal interference [4].

-145 dBW/Hz

-163.5 dBW/Hz

Residential environment described in ITU-R  P.372-8, Table 1.

-122 dBW/Hz

-140.5 dBW/Hz

Noise level at 14 MHz, calculated from the FCC §15.107(a) radiated emissions limits.[5]

 

1.4              The noise levels were entered into VOACAP in dBW/Hz on 3 MHz. VOACAP extrapolates this to other frequencies per Formula 11 listed in Section 5 of ITU-R P.372-8.

 

2.                  Bandwidth: The levels of man-made noise described in ITU-R P.372-8 are expressed in dBW/Hz.  VOACAP extrapolates this to real receiver bandwidth by having the user set the appropriate “Required Signal to Noise” parameter. The required signal-to-noise ratio referenced to dBW/Hz used in VOACAP was conservatively based on a receive bandwidth of 2500 Hz, plus a modest 10 dB signal/noise ratio, for a value of 44 dB required SNR referenced to 1 Hz bandwidth.

 

3.         Part-15 Emissions Noise Levels:

 

3.1              ARRL has previously provided to the FCC calculations[6] that show that BPL deployed at the present §15.107(a) limits will create man-made noise levels of up to approximately 60 dB greater than the ambient noise levels at many amateur stations. For the calculations in this paper, ARRL will conservatively estimate that BPL operating at the FCC emissions limits of +29.5 dBuV/m at 30 meters distance from the radiating source will have a peak-envelope power[7] received signal level (RSL) of:

 

RSLdBW/Hz = -107.2 + 29.5 dBuV/m - 20log10(FMHz) + rcv ant gain  0 dBi – 10log10(9000 Hz)

 

3.2              This calculation results in a RSLdBW/Hz  of –140.2 dBW/Hz on 14 MHz and –131 dBW/Hz on 5 MHz for isotropic antennas placed in fields that are at the §15.107(a) limit of +29.5 dBuV/m.  These antennas are conservatively presumed to be 30 meters from the radiating source.

 

4.         Analysis of Results:

 

4.6         ARRL has included all of the graphs from its calculations at the end of this document. To analyze the impact of the results of this study in the following discussion, ARRL has chosen samples from the set of graphs that best represent the overall results. 

 

4.2       ARRL has reached the following conclusions:

 

4.3              Figure 1 shows the results of using the VOACAP inverse-area coverage program to calculate the percentage of time that signals from stations located at various places around the world will be at least as strong as the required signal/noise ratio entered into the program.  ARRL chose a required signal/noise ratio of 44 dB, representing 10 dB over the noise level in a 2500 Hz bandwidth. Figure 1 is based on measurements of man-made noise levels at amateur stations in Connecticut in 1996. This level was typically     –170 dBW/Hz on 14 MHz.  The VOACAP software combines the programmed man-made noise level with the predicted natural-noise levels for the geographic location, time of year, time of day and frequency and calculates reliability of a circuit, using the parameters provided. ARRL chose a transmit power level of 30 dBW EIRP (1 kW) to represent a typical amateur station using 100 watts PEP transmitter power and a 3-element Yagi antenna at a reasonable height.[9]

 

4.4              The reliability is shown on the charts in color. Each chart has the color contours explained in the upper right side of the chart.


 

Figure 1.  This shows the calculated reliability in percent for an ambient man-made noise level of  –170 dBW/Hz on 14 MHz.   The station in this model is using a 3-element Yagi[10] to receive signals from world-wide stations transmitting  +30 dBW EIRP.  This station is capable of worldwide communication at various times of day.  Date: Oct 01 2000 UTC  SSN = 50.[11]

 

4.5              The ITU-R P378.2 recommendation describes an ambient man-made noise level of –145 dBW/Hz for residential environments.  This is somewhat higher than the levels ARRL used for its Figure-1 calculation. The ITU-R level is the median value of the measured results.  The present nature of much man-made noise is such that all devices that radiate noise do not all radiate at the same time, or even all the time, in most cases. Most do not radiate equally on all frequencies. For example, a computer system may be a prolific generator on RF, but much of that energy if found on specific frequencies, with most spectrum being relatively clear. Nonetheless, ITU-R P.372-8 does represent the worldwide consensus of the present level of man-made noise from the types of devices and geographical distribution found in the environment measured.

 

4.6         Figure 2 shows that at the man-made noise levels in ITU-R P.372-8, there is a demonstrable degradation to the reliability and range of world-wide HF communications, compared to the results from a quieter location shown in Figure 1.

 

 

Figure 2.  This shows the calculated reliability in percent for an ambient man-made noise level of –163.5 dBW/Hz, the ITU-R P372-8 level for “residential” environments at 14 MHz.  The station in this model is using a 3-element Yagi to receive signals from worldwide stations transmitting 30 dBW EIRP.  Although still capable of worldwide communications, the present level of man-made noise is just starting to have a significant effect on the capability of this station to establish reliable communications.  Date: Oct 01 2000 UTC SSN = 50. 

 

4.7         Any changes in regulations for unlicensed emitters on HF, or in the nature of devices that are deployed under the existing regulations, will have an impact on the median values of man-made noise. Even a small increase can have a severe effect on HF communications circuits.  Figure 3 shows a graph of the reliability of HF communications with a modest 10 dB increase in the median value of man-made noise over the ITR-R P.372-8 levels for man-made noise.


 

Figure 3.  This shows the calculated reliability in percent for an ambient man-made noise level of  –153.5 dBW/Hz on 14 MHz, a modest 10 dB higher than the ITU-R P372-8 median noise level for “residential” environments at 14 MHz.  The station in this model is using a 3-element Yagi to receive signals from worldwide stations transmitting 30 dBW EIRP.  The ability to overlay other uses on top of HF communications over existing worldwide HF communications is tottering on the brink of degradation.  This modest change in noise levels from the present environment has changed the 14-MHz spectrum region from a worldwide to a regional band. Date: Oct 01 2000 UTC  SSN = 50. 

 

4.8         Part 15 regulations set limits on the emissions of devices to control man-made noise. However, the regulations need to be used carefully to ensure that this continues to be the case.  Figure 4 shows the effect on HF communications circuits of noise levels at the limits of Part 15.


 

 

Figure 4.  This shows the calculated reliability in percent for an ambient man-made noise level of –140.4 dBW/Hz on 14 MHz, the level of signal that would be received by an isotropic antenna placed in a field at the present level of Part-15 radiated emissions for carrier-current devices.  The station in this model is using a 3-element Yagi to receive signals from worldwide stations transmitting +30 dBW EIRP.   The range and reliability of this station on 14 MHz has been reduced to the point where this frequency range is no longer useful for long-distance communication. Date: Oct 01 2000 UTC  SSN = 50. 

 

5.         Other Frequencies

 

5.1              The degradation to HF communications is not limited to 14 MHz.  The following figures show the difference between regional communication on 5 MHz with an ambient man-made noise level from the residential environment described in ITU-R P.372-8 and a man-made noise level as described by the maximum radiated emissions Part-15 limits that apply to carrier-current devices. 

 

Figure 5.  This shows the calculated reliability in percent for an ambient man-made noise level of –138.9 dBW/Hz at 5 MHz, the ITU-R P372-8 man-made noise level for “residential” environments at that frequency.  The station in this model is using a half-wave dipole to receive signals from regional stations using +20 dBW EIRP on 5 MHz.[12] 

Date: Mar 01 0000 UTC   SSN = 50.

 

Figure 6.  This shows the calculated reliability in percent for an ambient man-made noise level of  –138.9 dBW/Hz at 5 MHz, the level of signal that would be received a that frequency by an isotropic antenna placed in a field at the present level of Part-15 radiated emissions for carrier-current devices.  The station in this model is using half-wave dipole to receive signals from regional stations using +20 dBW EIRP on 5 MHz. 

Date: Mar 01   Time: 0000 UTC   SSN = 50. 

 


6.         BPL and Carrier-Current Devices

 

6.1              The models show that the widespread deployment of BPL systems under the present Part 15 rules would cause significant degradation of HF communications in areas that are near these systems. Unlike most devices regulated by Part 15 in use now, BPL systems are not limited to a single, small geographical area, but will occupy entire communities.  BPL systems are not going to be used only for relatively short periods of time, but will see long-term and continuous use in most deployments. Many uses of BPL will include continuous connections to the Internet and streaming video, to name just a few applications that will keep BPL systems emitting all of the time.[13] Unlike the present environment, where the emissions from most Part 15 devices that occur at the FCC limits often occur on discrete frequencies that can be avoided by a frequency-agile radio service, the emissions from BPL systems will be at a virtually constant level across all spectrum being used by BPL systems.  

 

6.2              For all these reasons, the degradation of HF communications as shown in Figures 4, 6 and the complete set of figures from these calculations at the end of this document is a reasonable representation of what to expect from the widespread deployment of BPL systems operating at the radiated emissions limits of the present rules. 

 

7.         Conservative Assumptions

 

7.1              All of the estimates used for this paper are intentionally conservative.  For example, although ARRL modeled the ability to receive worldwide stations of 30 dBW EIRP, many amateur stations utilize lower power or lower gain antennas.  EIRP of 20 dBW is not at all uncommon and a growing number of low-power enthusiasts operate at power levels below 10 dBW EIRP.  Although amateurs can operate at transmitter power levels of up to 31.8 dBW, FCC Part 97 rules require the use of the minimum-necessary power level.

 

7.2              The noise levels ARRL measured in Newington, CT are not as low as those found in the more quiet locations in use by some amateur operators.  Many amateur operators have invested in quiet home locations to ensure that they have maximum communications capability. Just as an example, in the 1996 study that ARRL used to provide its estimate of the ambient noise level near W1AW in Newington, CT, ARRL measured a station in Somers, CT at an ambient noise level of –179 dBW/Hz on 14 MHz.  Other stations are in even more quiet areas. These stations would generally have better communications capability than the examples used in this paper.

 

7.3              The noise levels ARRL used in VOACAP are referenced to an isotropic receive antenna.  VOACAP, however, adds the programmed gain (7.5 dBi on 14 MHz and 2.14 dBi on 5 MHz) to the received signal, but not the noise. In practice, the received noise level at the amateur station would also be increased over the levels ARRL assumed, if the antenna’s directivity has gain in the direction of the noise source.

 

7.4              ARRL also presumed that the receive antenna was located 30 meters away from the noise source.  A recent, albeit informal, survey on the ARRL web page indicates that over 50% of amateurs have antennas that are located closer than 30 meters to overhead power lines[14]. ARRL’s calculations indicate that the noise level near power lines will increase at approximately a 20 dB / distance decade ratio. This is a conservative estimate, compared to the methods the rules permit, which is to presume that the field strength varies at a 40 dB / distance decade ratio.

 

7.5              ARRL believes that it was not necessary to include all of these additional factors of closer antennas in this paper, because the conservative assumptions that ARRL used clearly demonstrate that HF communications would be significantly degraded by nearby BPL systems operating at the present FCC limits.  If included, the less conservative assumptions, which do apply very well to routine amateur operation, would show results that are typically 20 to 40 dB worse than what is presented in this paper.  Some amateur stations would require even more protection if the existing capability of the Amateur Radio Service it to be maintained intact.

 

8. The complete set of VOA graphs for various times of year and day follow[15].


Noise level:  –170 dBW/Hz at 14 MHz.  Date: Jan 01  Time: 0000 UTC  SSN = 50

Noise level:  Residential at 14 MHz   Date: Jan 01  Time: 0000 UTC  SSN = 50

Noise level:  Residential + 10 dB at 14 MHz.  Date: Jan 01  Time: 0000 UTC  SSN = 50

Noise level:  Part 15 limits at 14 MHz.  Date: Jan 01  Time: 0000 UTC  SSN = 50

Noise level:  –170 dBW/Hz at 14 MHz.  Date: Jan 01  Time: 0400 UTC  SSN = 50

Noise level:  Residential at 14 MHz   Date: Jan 01  Time: 0400 UTC  SSN = 50

Noise level:  Residential + 10 dB at 14 MHz.  Date: Jan 01  Time: 0400 UTC  SSN = 50

Noise level:  Part 15 limits at 14 MHz.  Date: Jan 01  Time: 0400 UTC  SSN = 50

Noise level:  –170 dBW/Hz at 14 MHz.  Date: Jan 01  Time: 0800 UTC  SSN = 50

 

Noise level:  Residential at 14 MHz   Date: Jan 01  Time: 0800 UTC  SSN = 50

Noise level:  Residential + 10 dB at 14 MHz.  Date: Jan 01  Time: 0800 UTC  SSN = 50

 

Noise level:  Part 15 limits at 14 MHz.  Date: Jan 01  Time: 0800 UTC  SSN = 50

Noise level:  –170 dBW/Hz at 14 MHz.  Date: Jan 01  Time: 1200 UTC  SSN = 50

Noise level:  Residential at 14 MHz   Date: Jan 01  Time: 1200 UTC  SSN = 50

 

Noise level:  Residential + 10 dB at 14 MHz.  Date: Jan 01  Time: 1200 UTC  SSN = 50

Noise level:  Man-made noise at Part 15 limits at 14 MHz.  Date: Jan 01  Time: 1200 UTC  SSN = 50

Noise level:  –170 dBW/Hz at 14 MHz.  Date: Jan 01  Time: 1600 UTC  SSN = 50

 

Noise level:  Residential at 14 MHz   Date: Jan 01  Time: 1600 UTC  SSN = 50

Noise level:  Residential + 10 dB at 14 MHz.  Date: Jan 01  Time: 1600 UTC  SSN = 50

 

Noise level:  Part 15 limits at 14 MHz.  Date: Jan 01  Time: 1600 UTC  SSN = 50

 

Noise level:  –170 dBW/Hz at 14 MHz.  Date: Jan 01  Time: 2000 UTC  SSN = 50

Noise level:  Residential at 14 MHz   Date: Jan 01  Time: 2000 UTC  SSN = 50

Noise level:  Residential + 10 dB at 14 MHz.  Date: Jan 01  Time: 2000 UTC  SSN = 50

Noise level:  Part 15 limits at 14 MHz.  Date: Jan 01  Time: 2000 UTC  SSN = 50


Noise level:  –170 dBW/Hz at 14 MHz.  Date: Apr 01  Time: 0000 UTC  SSN = 50

Noise level:  Residential at 14 MHz   Date: Apr 01  Time: 0000 UTC  SSN = 50

Noise level:  Residential + 10 dB at 14 MHz.  Date: Apr 01  Time: 0000 UTC  SSN = 50

 

Noise level:  Part 15 limits at 14 MHz.  Date: Apr 01  Time: 0000 UTC  SSN = 50

Noise level:  –170 dBW/Hz at 14 MHz.  Date: Apr 01  Time: 0400 UTC  SSN = 50

Noise level:  Residential at 14 MHz   Date: Apr 01  Time: 0400 UTC  SSN = 50

Noise level:  Residential + 10 dB at 14 MHz.  Date: Apr 01  Time: 0400 UTC  SSN = 50

Noise level:  Part 15 limits at 14 MHz.  Date: Apr 01  Time: 0400 UTC  SSN = 50

Noise level:  –170 dBW/Hz at 14 MHz.  Date: Apr 01  Time: 0800 UTC  SSN = 50

Noise level:  Residential at 14 MHz   Date: Apr 01  Time: 0800 UTC  SSN = 50

Noise level:  Residential + 10 dB at 14 MHz.  Date: Apr 01  Time: 0800 UTC  SSN = 50

Noise level:  Part 15 limits at 14 MHz.  Date: Apr 01  Time: 0800 UTC  SSN = 50

Noise level:  –170 dBW/Hz at 14 MHz.  Date: Apr 01  Time: 1200 UTC  SSN = 50

Noise level:  Residential at 14 MHz   Date: Apr 01  Time: 1200 UTC  SSN = 50

Noise level:  Residential + 10 dB at 14 MHz.  Date: Apr 01  Time: 1200 UTC  SSN = 50

Noise level:  Part 15 limits at 14 MHz.  Date: Apr 01  Time: 1200 UTC  SSN = 50

Noise level:  –170 dBW/Hz at 14 MHz.  Date: Apr 01  Time: 1600 UTC  SSN = 50

Noise level:  Residential at 14 MHz   Date: Apr 01  Time: 1600 UTC  SSN = 50

Noise level:  Residential + 10 dB at 14 MHz.  Date: Apr 01  Time: 1600 UTC  SSN = 50

Noise level:  Part 15 limits at 14 MHz.  Date: Apr 01  Time: 1600 UTC  SSN = 50

Noise level:  –170 dBW/Hz at 14 MHz.  Date: Apr 01  Time: 2000 UTC  SSN = 50

Noise level:  Residential at 14 MHz   Date: Apr 01  Time: 2000 UTC  SSN = 50

Noise level:  Residential + 10 dB at 14 MHz.  Date: Apr 01  Time: 2000 UTC  SSN = 50