[USCC] carbon sequestration via composting
Matthew Cotton
mattcotton at mindspring.com
Fri Jan 18 10:15:50 CST 2008
Brenda -
One of the best sources on this currently is a Life-Cycle Assessment
done by the Recycled Organics Unit of the University of New South
Wales in Australia (Available as a download here: http://
www.recycledorganics.com/publications/reports/lca/lca.htm)
They looked at carbon sequestration in composted soil amendment
applied to cotton (the crop) and composted mulch applied to grapes.
In cotton, they report
• "Sequestering about 2.9-5.9 tons of carbon per hectare after 10
years. This figure may be taken for carbon accounting process.
• Sequestering about 1.8-3.5 tons of carbon per hectare after 100
years. This figure is relevant to LCI studies."
For grapes:
• "Sequestering about 11.56 tons of carbon per hectare after 10
years. This figure may be taken for carbon accounting process.
• Sequestering about 7.056 tons of carbon per hectare after 100
years. This figure is relevant to LCI studies."
There is more relevant data in Section 7.6 of the report. Keep in
mind that compost feedstock, how it was composted, soil type, crop
type, growing practices, and climate probably all play a role in
relatively long-term carbon sequestration in soil.
The good news is that while the GHG gains one gets from carbon
sequestration may not be that great (compared to the methane
avoidance) adding compost to soil has so many other benefits, many of
which have not been quantified adequately.
Hope this is useful.
Matthew Cotton
Integrated Waste Management Consulting, LLC
19375 Lake City Road
Nevada City, CA 95959
(530) 265-4560
Fax (530) 265-4547
matt at mattcotton.com
www.mattcotton.com
Join us at the US Composting Council's 16th Annual Conference & Trade
Show, February 9 - 12th, 2008 at the Oakland Marriott City Center,
Oakland, California. Check it out at www.compostingcouncil.org
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Carbon Sequestration: Position of the Soil Science Society of America
Increased long term (20-50 year) sequestration of carbon in soils,
plants and plant products will benefit the environment and
agriculture. Crop, grazing, and forestlands can be managed for both
economic productivity and carbon sequestration. In many settings this
dual management approach can be achieved by applying currently
recognized best management practices such as conservation tillage,
efficient nutrient management, erosion control, use of cover crops
and restoration of degraded soils. In addition, conversion of
marginal arable land to forest or grassland can rapidly increase soil
carbon sequestration. Research is needed that better quantifies
carbon sequestration obtained by these practices; this research
should culminate in a scientifically defensible soil carbon
sequestration accounting system that also would be suitable to the
business sector, should soil carbon become a marketable commodity.
Implementation of these practices will integrate a wide range of
disciplines in the basic, agricultural, silvicultural, and
environmental sciences as well as in the social, economic and
political sciences. SSSA advocates a global increase in soil organic
matter as a timely benefit to global well being by reducing the rate
of increase in atmospheric CO2 and increasing the productivity of
soil, particularly in many areas with degraded soils.
What is carbon sequestration?
Carbon sequestration refers to the storage of carbon in a stable
solid form. It occurs through direct and indirect fixation of
atmospheric CO2. Direct soil carbon sequestration occurs by inorganic
chemical reactions that convert CO2 into soil inorganic carbon
compounds such as calcium and magnesium carbonates. Direct plant
carbon sequestration occurs as plants photosynthesize atmospheric CO2
into plant biomass. Subsequently, some of this plant biomass is
indirectly sequestered as soil organic carbon (SOC) during
decomposition processes. The amount of carbon sequestered at a site
reflects the long-term balance between carbon uptake and release
mechanisms. Many agronomic, forestry, and conservation practices,
including best management practices, lead to a beneficial net gain in
carbon fixation in soil.
What is the relationship between carbon sequestration, land
management and other environmental factors?
The implementation of effective land management practices, especially
through stewardship activities such as the Conservation Reserve
Program, Wetland Reserve Program, Forestry Incentive Program and
conservation tillage, lead to both increased above ground carbon
sequestration and to increased SOC. Soils gaining SOC are also
generally gaining in other attributes that enhance plant productivity
and environmental quality. Increases in SOC generally improve soil
structure, increase soil porosity and water holding capacity, as well
as improve biological health for a myriad of life forms in soil.
In general there is a favorable interplay between carbon
sequestration and various recommended land management practices
related to soil fertility (e.g., adding mineral fertilizers, manures,
sludges and biosolids), tillage, grazing, and forestry. Recommended
agronomic, grazing land and forestry practices also enhance land
sustainability, wildlife habitat and water quality. In most
locations, especially environmentally sensitive settings, these
practices also result in decreased water and wind erosion that
degrade soil carbon stocks. The same positive relationship that
exists between carbon sequestration and recommended land management
can, in some settings, improve water quality and aid wildlife habitat
restoration.
Why include soils in carbon sequestration?
Worldwide, SOC in the top 1 meter of soil comprises about 3/4 of the
earth's terrestrial carbon; nevertheless, there is tremendous
potential to sequester additional carbon in soil. For example, many
cropland soils of the United States have lost as much as 50% of their
original SOC due to the effects of land clearing and tillage. Such
conventional farming practices "burn" SOC just as we burn fossil
fuels today. However, in the case of SOC this historical decline can
be reversed, which is not the case for fossil fuel reserves. With
proper management the US can put back much of the SOC depleted over
the past two centuries. Improved management of crop, grazing, and
forest lands is estimated to potentially offset 30,000-60,000 million
metric tons of the carbon released by fossil fuel combustion over the
next 50 years.
What else do we know today about US emissions and US sequestration of
carbon?
CO2 emissions make-up more than 80% of all greenhouse gas emissions
in the US with the annual input of C in the atmosphere being about
1,900 million metric tons. Most of this C is a product of burning
fossil fuels (from USDOE).
US forestlands currently fix about 250 million metric tons of
atmospheric C each year (from USDA-FS and USDOE).
US cropland can sequester about 75-200 million metric tons of
atmospheric C per year by using current best management practices. US
grazing land can sequester 30-90 million metric tons of atmospheric C
annually by controlled grazing, fire management, and by use of
fertilizers and improved cultivars (from USDA Global Change Fact Sheet).
Progressive research on carbon sequestration is ongoing and a
priority in a number of federal and state agencies as well as many
universities with soil science, agronomy, forestry and allied
departments.
What still needs to be known?
Improvement in monitoring and verification protocols for carbon
sequestration in soil-plant ecosystems is needed for quantitative
economic and policy analyses. These protocols need to be
quantitatively defensible and readily applicable to fields and
watersheds with differing land uses and weather conditions. Such
protocols must be acceptable, both domestically and internationally,
to scientists, policy makers, landowners, and business groups. These
protocols must be suitable for use by employees of government
agencies and licensed professionals.
Practical techniques to quantify the overall net beneficial impact of
agricultural and silvicultural practices on all greenhouse gases,
including methane (CH4) and nitrous oxide (N2O), are needed. Other
beneficial services derived from improved land practices, such as
changes in soil quality, productivity, water and air quality, and
erosion must also be recognized and evaluated. Recommended carbon
sequestration practices must show benefit for the total environment
from a whole ecosystem accounting perspective.
Plant breeders and physiologists must be involved to insure that
cultivars developed for economic and biological yields also improve
soil. The biological yield of above and below ground biomass should
have properties, such as elevated lignin and suberin contents that
promote accumulation of stable carbon forms in soil and in plant
products.
The potential impact of climate variability on the stability of
sequestered carbon in soils and long-lived plants must be evaluated.
Determination of suitable land management practices is needed to
minimize risk of carbon release from soil in response to changes in
regional weather patterns such as El Niño and La Niña.
Long-term studies are needed to insure that currently effective
carbon sequestration practices result in stable carbon forms for the
long term (at least 20-50 years).
A soil carbon economy: A timely opportunity for all Nations
The economic value of soil carbon needs to be assessed with
consideration for both onsite and offsite effects. Procedures are
needed for a defensible soil carbon accounting system, and policies
need to be established that provide incentives for net soil carbon
sequestration at the global scale. Such policies can provide
financial incentives for the restoration of degraded and impoverished
soils, while achieving reductions in the rate of buildup of
atmospheric CO2 levels. Enhancing the SOC pool through global and
national policy incentives may be especially beneficial to improving
agronomic productivity, enhancing food security and reducing poverty
in countries with degraded soils, thus providing splendid benefits to
humankind. The dynamics of carbon sequestration processes must be
evaluated in the context of local soil and crop attributes including
biogeochemical cycles and soil spatial variability. Accounting for
variability of soil and plant processes is needed at a range of
scales from fields to watersheds and from regional to continental
scales. Spatial and temporal variability of soil C is known to be
high in many areas. Any soil C commodity price structure will need to
be conservatively discounted for soil C variability.
Incentives and plans for adoption of sound technical practices are
needed for farmers, ranchers, foresters and other land managers.
Implementation of such plans will require better understanding of
rural society and the market incentives needed for adopting changes
in farming, grazing, and forestry practices that benefit all sectors
of society.
Advancement in knowledge through targeted research will permit
refined quantitative assessment of the total carbon sequestration
potential of the US and our global partners.
Prepared by SSSA Ad Hoc Committee S893
Lee Burras, Iowa State University (Chair)
H.H. Cheng, University of Minnesota
John M. Kimble, USDA-NRCS
David E. Kissel, The University of Georgia
Rattan Lal, The Ohio State University
Robert J. Luxmoore, Oak Ridge National Laboratory
Maurice J. Mausbach, USDA-NRCS
Charles W. Rice, Kansas State University
Goro Uehara, University of Hawaii
Lawrence P. Wilding, Texas A&M University
Approved by SSSA Board of Directors
Robert J. Luxmoore
SSSA President
October 25, 2001
Date
On Jan 17, 2008, at 1:48 PM, Brenda Platt wrote:
> I am writing a booklet tentatively called, Stop Wasting the
> Climate, and
> need some good citations on carbon sequestration via composting.
>
> Can any one point me to data showing how much of the carbon in
> composted
> organics typically gets sequestered in the compost product vs C02?
>
> I found one article that indicated approx. half the carbon is
> sequestered.
> This article cited Elliot Epstein's 1997 book, The Science of
> Composting,
> (pp. 487). Can someone confirm this?
>
> Thanks in advance!
>
> Brenda
>
> --
> Brenda Platt
> Institute for Local Self-Reliance
> 927 15th Street, NW, 4th Fl
> Washington, DC 20005
> 202-898-1610 ext. 230
> www.ilsr.org
> _______________________________________
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