tion from discarded LIB systems. Accidental
inclusion of LIBs in lead battery recycling has
proven hazardous, and better safety and recy-
clinge protocols are needed.
The range of tools and methods developed
over the past 30 years, both experimentally
and theoretically, are readily applicable to
further develop and elucidate the science
of lead–acid batteries. These topics would
greatly benefit from further engagement
from U.S. National Laboratories and across
academia ( 15 ). Leveraging our current sci-
entific knowledge and an established manu-
facturing industry with admirable safety and
recycling records would ensure
strong economic, technical, and
sciencemag.org SCIENCE
GRAPHIC: MELISSA THOMAS BAUM/
SCIENCE
Perhaps the best prospect for the unuti-
lized potential of lead–acid batteries is elec-
tric grid storage, for which the future market
is estimated to be on the order of trillions
of dollars. For that reason, the low cost of
production and materials, reduced concerns
about battery weight, raw material abun-
dance, recyclability, and ease of manufactur-
ing make it an attractive solution if technical
barriers can be addressed. At a current spot
price below $2/kg and an average theoretical
capacity of 83 ampere hours (Ah)/kg (which
includes H 2 SO 4 weight and the average con-
tribution from Pb and PbO 2 active materials)
that rivals the theoretical capac-
ity of many LIB cathode materi-
als ( 8 ), lead–acid batteries have
the baseline economic potential
to provide energy storage well
within a $20/kWh value ( 9 ).
Despite perceived competition
between lead–acid and LIB tech-
nologies based on energy density
metrics that favor LIB in por-
table applications where size is
an issue ( 10 ), lead–acid batteries
are often better suited to energy
storage applications where cost is
the main concern. In reality, LIB
technology has been more detri-
mental to nickel–metal hydride
and nickel-cadmium battery mar-
kets ( 3 ). The increased cost, small
production rates, and reliance on
scarce materials have limited the
penetration of LIBs in many en-
ergy storage applications.
The inherent concern sur-
rounding lead–acid batteries
is related to the adverse health
and environmental effects of
lead ( 11 ). More effective mitiga-
tion is feasible with application
of known practices, strict gov-
ernment regulations, and im-
proved training and engineering
controls, which would further
increase the already impressive
recycling rate of 99% ( 12 ). Also,
many serious safety and health
concerns exist as part of LIB
manufacturing and operation,
including the carcinogenic po-
tential of Ni and Co oxide com-
ponents of cathode materials,
the production of highly toxic or-
ganofluorophosphate neurotox-
ins as a consequence of thermal
runaway events (battery fire and
explosion) ( 8 , 13 ) and potential
contamination of the environ-
ment with toxic organofluorine
by-products arising from electro-
lytes and additives ( 14 ).
As with any technology, many of the as-
sociated risks can be limited with proper
management of materials, good manufactur-
ing practices, and committed waste manage-
ment. The 99% recycling rate of lead–acid
batteries ( 12 ) and stringent regulations on Pb
environmental emissions greatly minimize
the risk of Pb release to the environment.
Alternatively, the lack of economically fea-
sible recycling solutions to LIB technology in
the short term, combined with the expected
increase in the number of battery cells that
are approaching their end of life, aggravate
the potential for environmental contamina-
INSIGHTS | PERSPECTIVES
Nanostructural
crystal formation
(~10 nm to ~10 μm)
Continuous dissolution
and redeposition of
active materials occur
at the surface of
particles and drive
changes in
microstructure.
Microstructural
and fuid fows
(10 μm to 1 mm)
Charge and discharge
cycles form complex
particle interfaces
between Pb and PbSO 4 or
PbO 2 and PbSO 4 on the
micrometer scale. These
self-structured porous
networks create acid and
water concentration
gradients at the
electrochemical
interfaces.
Water-splitting
reactions
(0.1 to 1 nm)
Charging can also split
water into H 2 and O 2 during
overcharging or at impurity
metal (M) atom.
Macroscopic
components
(centimeters)
The Pb anode and
PbO 2 cathode
electrodes and
separator are
illustrated. Charging
regenerates these
materials.
Negative electrode Separator Positive electrode
panel
Pb+C
grid
Pb paste
PbO 2 paste
Pb-alloy
grid
H 2 SO 4
concentration
Electrode
grid Mber
H 2 O
concentration
PbSO 4
Pb/PbO 2
H 2 O
dilution
H 2 SO 4
dilution
e–
Pb
2H+ H 2
2e–
2H 2 OO 2
4H+ + 4e–
μm)
n
H 20
Discharge
Charge
PbSO 4
H 2 SO 4
2e–
PbO2 (positive)
Pb (negative)
Detail below
Detail
below
M
environmental support for lead–
acid batteries to continue serv-
ing as part of a future portfolio
of energy storage technologies. j
REFERENCES AND NOTES
1. I. Fe l d m a n et al., Environ. Law Rep. 46
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ACKNOWLEDGMENTS
The approach applied to develop structure-
function correlations was funded by the U.S.
Department of Energy, Office of Science,
Office of Basic Energy Sciences, Materials
Sciences and Engineering Division. The
research efforts were supported by the Lead
Battery Science Research Program through
a Cooperative Research and Development
Agreement. Use of the Center for Nanoscale
Materials, an Office of Science user facility,
was supported by the U.S. Department
of Energy, Office of Science, Office of
Basic Energy Sciences, under contract
no. DE-AC02-06CH11357. We thank E.
Coleman, D. Strmcnik, M. Zorko, C. Ferels, N.
Chaudhari, and in memoriam Stefan Djokic
for support in experiments.
10.1126/science.abd3352
Multiscale electrochemistry
The technical challenges facing lead–acid batteries are a consequence of the
complex interplay of electrochemical and chemical processes that occur at
multiple length scales. Atomic-scale insight into the processes that are taking
place at electrodes will provide the path toward increased efficiency, lifetime, and
capacity of lead–acid batteries.
924 21 AUGUST 2020 • VOL 369 ISSUE 6506
Published by AAAS