United States Environmental Protection Agency National Risk Management Research Laboratory Cincinnati, OH 45268 Research and Development EPA/600/SR-98/056 July 1998 Project Summary Demonstration of the Environmental and Demand-side Management Benefits of Grid-connected Photovoltaic Power Systems - 1994-1997 Daniel L. Greenberg, Edward C. Kern, Jr., Miles C. Russell, and Priscilla D. Kern The report gives results of an inves- tigation into the pollutant emission re- duction and demand-side management potential of 12 photovoltaic (PV) sys- tems that began operation between June 1994 and July 1996 in various locations in the U.S. The project was sponsored by the U.S. EPA and 12 elec- tric utilities. The report documents the project and presents analyses of each system's ability to offset emissions of sulfur dioxide, nitrogen oxides, and car- bon dioxide, and to provide power dur- ing peak load hours for the host buildings and the participating utilities. The analyses indicate a broad range in emission offsets resulting from PV system operation due to variation in the solar resource available to each system and variation in the marginal emission rates of the participating utili- ties. Each system's ability to provide power during peak load periods is in- vestigated using gross and net (of PV generation) load duration curves. Dif- ferences between these curves provide insight into each PV system's ability to reduce the highest loads experienced by the host building or utility. One set of such curves is presented for each sys- tem and for each month of a 12-month performance monitoring period. This Project Summary was developed by the National Risk Management Re- search Laboratory's Air Pollution Pre- vention and Control Division, Research Triangle Park, NC, to announce key find- ings of the research project that is fully documented in a separate report of the same title (see Project Report ordering information at back). Introduction In May 1993 the U.S. EPA issued the second of three solicitations for the instal- lation of grid-tied PV systems with the goal of measuring their environmental and demand-side benefits. Following up on its success with the first solicitation, As- cension Technology's proposal was again selected from the proposals submitted. Ascension's proposal was supported by 12 electric utilities, all of which ulti- mately participated in the project by in- stalling a PV system. The participating utilities were 1) Boston Edison Company (BECO), serving the greater Boston area; 2)Public Service of Oklahoma (PSO), which has three service areas in eastern and central Oklahoma; 3) Consolidated Edison (CONED), serving New York City and Westchester County, New York; 4) Idaho Power Corporation (IPC), serving most of Idaho; 5) New York State Electric and Gas (NYSEG), with service areas concentrated in western New York state, 6) Nevada Power Company (NPC), serv- ing Las Vegas and southern Nevada; 7) the Los Angeles Department of Water and Power (LADWP), which serves Los An- geles; 8) Public Service Company of Colo- rado (PSCO), serving Denver and other urban areas of Colorado; 9) the Arizona ------- Electric Power Co-Operative (AEPCO), which serves rural areas in southern Ari- zona; 10) Florida Power Corporation (FPC), serving the panhandle and gulf coast of Florida; 11) Atlantic Energy (ACE) (formerly Atlantic City Electric), which serves southern New Jersey; and 12) Duke Power (Duke), with a service area covering central and eastern North Caro- lina. In addition to the geographic diver- sity of the service areas represented by these utilities, their pollutant emission characteristics also proved to be quite divergent. Ascension Technology's part- ners from the PV industry were ASE Americas, which provided PV modules, and Omnion Power Engineering Corpo- ration, which provided the inverters. EPA awarded the contract for this project to Ascension Technology in Sep- tember 1993. The final system design ef- fort began shortly thereafter, and the first system was installed and operating in May 1994. Installations of the remaining 11 systems were completed over the course of the next 2 years. Monitoring of each system began con- currently with initial system operation, al- though the "official data start date" was delayed at sites where there were initial technical problems with either instrumen- tation or PV system hardware. At each site, 15-minute average values of solar irradiance, ambient temperature, PV sys- tem power output, and building load were recorded and stored for subsequent re- trieval by modem. Monitoring of each site for the purposes of this study continued for a period of 1 year. Emission rate and load data provided by each participating utility were used in conjunction with the data collected from each system to conduct analyses of (1) the ability of each PV system to reduce the peak power demand of the building on which it was installed; (2) the chrono- logical correlation of each PV system's power output to the respective utility's peak loads; and (3) the emission offsets resulting from operation of the PV sys- tems. Chapter 1 of this report provides a gen- eral introduction to the project. Chapter 2 describes the design, installation, and cost of each system. Chapter 3 describes the data acquisition system and presents data collection and review procedures. Chap- ter 4 describes the operating history and performance of each system in turn, and presents the results of the three analyses described above. Chapter 5 discusses the common operational problems en- countered by this set of PV systems, and reviews the results of the emission offset and load matching analyses across all 12 systems. The authors' conclusions re- garding the use of PV systems to offset pollutant emissions or for purposes of re- ducing peak building or utility loads are presented in Chapter 6. PV Systems All PV systems used in this project shared the same design but were installed in different parts of the country. Their per- formance, as measured by PV system outage, was affected by both systemic and environmental factors. System Design All PV systems installed under this project have a peak rating of 18 kW, and consist of three independent 6 kW sub- systems, each with its own inverter. The inverter in each subsystem is fed by three parallel source circuits, each consisting of 10 PV modules in series. There are thus 90 modules in each system. All 12 installations utilize Ascension Technology RoofJack PV array supports, which have been used to install more than 1 MW of PV systems. PV arrays are held in place by ballast on flat roofs; this approach re- quires no roof penetrations for hold-down of the PV arrays. System design details were developed in close cooperation with Mobil Solar (now ASE Americas, Inc.), the PV module supplier. Omnion Power Engineering was selected as the supplier of power conditioners. The PV systems were designed to accommodate the speci- fications of the 6 kW-rated Omnion Series 2200 unit. System Installation Although the typical installation took only 3-4 days to complete, the final sys- tem did not begin operation until nearly 2 years after the first system's installation was complete. This prolonged period was due to numerous siting and code compli- ance difficulties encountered in the pro- cess of installing the systems. With one exception, the systems were installed on the roofs of commercial and industrial buildings. The exception was the ground-mounted array on the cam- pus of the University of Nevada at Las Vegas (EPA23). Table 1 summarizes the location of each system. System Performance History Of the 12 PV systems installed by this project, all but one suffered one or more events during the study period which temporarily limited system output or pre- vented generation altogether. Inverter-re- Table 1. Participating Utilities and Installation Locations Site Name EPA 18 EPA 19 EPA 20 EPA 21 EPA 22 EPA 23 EPA 24 EPA 25 EPA 26 EPA 27 EPA 28 EPA 29 Utility BECO PSO CONED I PC NYSEG NPC LADWP PSCO AEPCO FPC ACE Duke Location Boston, MA Lawton, OK Greenburgh, NY Boise, ID East Aurora, NY Las Vegas, NV Los Angeles, CA Henderson, CO Benson, AZ Clearwater, FL Pomona, NJ Huntersville, NC lated problems were the most vexing of the generation-limiting events. In all, 22 inverter-related events resulted in a gen- eration loss of 12,200 kWh, approximately 3.3% of the combined generation of these systems over the relevant time periods. Snow cover was also a frequent cause of PV system outages for those systems lo- cated in northern locations or at high alti- tudes. Accurate estimation of generation losses due to snow cover is not possible because the sensor used to measure sun- light (the primary input to simulation of the systems' performance) was usually covered by snow when the arrays were. Only about 600 kWh of lost generation may be attributed specifically to module failures. Although such failures are known to have resulted in greater losses, it is not possible to separate these losses from those due to other equipment failures that occurred simultaneously. About 1,040 kWh (approximately 0.3% of gross gen- eration) were lost due to faults in array wiring or problems with source-circuit pro- tectors. Total generation by the PV sys- tems was reduced by another 6,650 kWh (1.8% of gross generation) due to failures in utility equipment. Results The report describes results of this project in terms of pollutant emission off- sets and load reductions for both the util- ity and the host building. Pollutant Emission Offsets Models of marginal emission rates (i.e., emission rates of load following units) were developed for each utility based on utility-provided data. The hourly emission ------- 500 400 "3 ^ ^ 300 o g 200 c < 100 0 n^ Tl 18 20 22 24 26 28 19 21 23 25 27 29 Site Number Figure 1. Annual Sulfur Dioxide Offsets. < 150 100 50 n 18 20 22 24 26 28 19 21 23 25 27 29 Site Number Figure 2. Annual Nitrogen Oxides Offsets. 60 "55 § 4° 0 ra 20 c < 10 0 ,— I — — — 18 20 22 24 26 28 19 21 23 25 27 29 Site Number Figure 3. Annual Carbon Dioxide Offsets. rates of sulfur dioxide (SO2), nitrogen ox- ides (NOX), and carbon dioxide (CO2) were then combined with hourly PV system generation data to determine hourly emis- sion offsets. Annual emission offsets are presented in Figures 1 through 3. Note that insuffi- cient data were provided to determine marginal emission rates for sites EPA23 and EPA28, and that generation by sys- tem EPA21 offset hydroelectric genera- tion and therefore resulted in zero offsets of all three pollutants. Aside from these three systems, annual SO2 offsets ranged from less than 80 g for a system offsetting generation by natural-gas-fired combus- tion turbines to 475 kg for a system that offset the generation of a coal-fired power plant. Annual NOX offsets ranged from 8 to 128 kg, and the range in annual CO2 emission offsets was from 16,700 to 50,400 kg. The extreme variability in these results is due to four factors: 1) the pollutant emission rates of each utility's load-fol- lowing generating units; 2) the installed capacity of the PV systems; 3) the local solar resource available to each system; and 4) the operating performance (i.e., reliability) of each system. Of these, utility emission rates were the most influential factor in determining offsets, particularly for SO2. The installed capacities of the 12 systems installed under this project were identical, and therefore did not play a role in inter-site differences in emission offsets, but variations in the solar resource and reliability of the systems certainly did. Since there are currently no mitigation measures in place for CO2, variation in utility CO2 emission rates is due only to the relatively small (about 2:1) variation in the carbon content of fuels used and variation in the heat rates of the power plants. The range of the highest to lowest annual offset is relatively small at 3.0. For the other pollutants, variations in the pol- lutant content of the fuel as well as inter- utility differences in type and efficiency of the load-following generators and in- stalled pollution mitigation equipment give rise to the tremendous differences be- tween utility emission rates which under- lie the differences in emission offsets described above. Host Building Load Reduction Each PV system's ability to provide power during building peak load hours was analyzed by comparing each building's monthly net (of PV generation) and gross load duration curves (LDC). The LDC is constructed by sorting all load values for a given period in descending order, and plotting each value against its rank in the sort. Differences in a building's net and gross LDC for the highest load values indicate the PV system's ability to provide power during peak load periods. Figure 4 presents an example of gross and net LDCs for one of the host build- ings. Some of the host buildings in this project had loads very well suited to peak- shaving by the PV system, while others always experienced their peak loads at times of low irradiance. During the 25 highest load hours in the months in which each host building experienced its high- est load (during the monitoring period), the average reduction in the building LDC ranged from 5 to 72% of system rating. Analysis of the data collected through this project revealed that the total annual 850 1 800 T3 (3 O 2 '5 750 700 Gross Load Net Load 0 5 10 15 20 25 Highest Building Load Hours Figure 4. Gross and Net LDCs. insolation available at a given location indicates little about the ability of a PV system to provide power during peak load hours. Several of the systems that pro- vided the most power during peak load hours also had among the lowest annual insolation. Conversely, some of the sites with the greatest solar resources proved to be among the worst load matchers in the group. Another conclusion resulting from this analysis is that a PV system's operation during one or a small number of peak building load hours may provide an inac- curate picture of that system's capacity ------- value. If a building's highest load(s) oc- cur during mid-day hours but the building also has near-peak loads occurring at times of low or no irradiance, the near- peak loalds will remain unaffected by the PV system, and will migrate upward in the building's net LDC. If the difference between the daytime peak load(s) and the nighttime near-peak load(s) is small relative the PV system's capacity, the dif- ference between the building's gross and net LDCs may be substantially smaller than the PV system's power generation during the daytime peaks. Conversely, if a PV system generates at a low capacity factor during the high- est building load hours, but provides more power at times when building load is near its peak level, it may be important to con- sider whether the conditions that resulted in the building's highest loads are repre- sentative of typical conditions for the build- ing. Use of gross and net LDCs allows one to review the effect of PV system opera- tion on as many or as few of the highest load hours as is desired, and is an es- sential tool in assessing the capacity value of a PV system. Utility Peak Load Reduction Conclusions regarding peak load re- duction at the utility system level are much the same as those discussed above for building peak load reduction. For some of the utilities participating in this study, PV systems can be very effective at pro- viding power during periods of peak load, while for other utilities whose peaks oc- cur at times of low or no irradiance, the technology provides little capacity value. In the months in which each utility's peak load occurred, the reductions of the utili- ties' LDCs over the 25 highest load hours ranged from zero to 71% of PV system rating. As discussed above for building load, the annual insolation available to a PV system has little to do with its ability to provide power when it is most needed. The three systems that had the highest levels of annual insolation yielded among the lowest LDC reductions during the utility's peak load month, and the system that provided the most support to its utility in the peak load month was ranked 10th in annual insolation. Finally, the use of chronological data alone to interpret the capacity value of PV may be deceiving. If near-peak utility loads occur at times of low irradiance, even a very large PV system (or set of systems) would do little to reduce the peak of the utility's LDC, even if that sys- tem operates at a high fraction of its rat- ing during the highest load hour or several hours. Again, in assessing the capacity value of PV systems, it is essential to determine how the resource would alter the utility LDC. ------- D. Greenberg, E. Kern, Jr., M. Russell, and P. Kern are with Ascension Technology, Inc., Lincoln, MA 01773. Ronald J. Spiegel is the EPA Project Officer (see below). The complete report, entitled "Demonstration of the Environmental and Demand-side Management Benefits of Grid-connected Photovoltaic Power Systems - 1994- 1997," (Order No. PB98-145311; Cost: $44.00, subject to change) will be available only from National Technical Information Service 5285 Port Royal Road Springfield, VA 22161 Telephone: 703-487-4650 The EPA Project Officer can be contacted at Air Pollution Prevention and Control Division National Risk Management Research Laboratory U.S. Environmental Protection Agency Research Triangle Park, NC 27711 United States Environmental Protection Agency CenterforEnvironmental Research Information Cincinnati, OH 45268 BULK RATE POSTAGES FEES PAID EPA PERMIT No. G-35 Official Business Penalty for Private Use $300 EPA/600/SR-98/056 ------- |