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

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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

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        18    20   22   24   26   28
          19   21   23   25   27    29
                Site Number

Figure 1.   Annual Sulfur Dioxide Offsets.
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                                              150
                                              100
                                               50
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        18    20   22   24   26   28
          19   21    23    25   27    29
                Site  Number

Figure 2.   Annual Nitrogen Oxides Offsets.
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        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

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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.

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  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

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