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THE EFFECTS OF HUMIC SUBSTANCES ON CROP PRODUCTION, SOIL, AND
WATER QUALITY
Mir-M. Seyedbagheri
University of Idaho Elmore County Extension
Mountain Home, Idaho
ABSTRACT
Soil organic matter has declined drastically in farmlands worldwide since 1900 as a result
of carbon turnover and cropping systems. Humic substances, a major constituent of soil organic
matter, are important for their influence on soil physical, chemical and biological properties that
are essential to soil health and plant growth, including chelation, mineralization, buffer effect,
clay mineral-organic interaction, and cation exchange. For the past 18 years we have evaluated
commercial humic acid products derived from lignite and leonardite in different cropping
systems. Research trials were established from 1990 through 2008 to evaluate the efficacy of
different humates products in potatoes in Western Idaho. Data from humic acids trials showed
that different cropping systems responded differently to different products in relation to yield and
quality. Important qualifying factors included source; concentration; processing; chelating or
complexing capacity of the humic acid products; functional groups (Carboxyl -CO2H; Phenol -
Ohp; Hydroxyl -Oha; Ketone -C=O; Ester O=C-O-R; Ether –C-O-C-; Amine –NH2,-NH,-N);
rotation and soil quality factors; consistency of the product in enhancing yield and quality of
crops; mineralization effect; and influence of the product on fertilizer use efficiency.
Collectively, the consistent use of good quality products in our replicated research plots in
different years resulted in a yield increase from 11.4 percent to the maximum of 22.3 percent.
Over the past decade, there has been a major increase in the quality of research and development
of organic and humic acids by some well-established manufacturers. Our experimentations with
these commercial products showed an increase in the yield and quality of crops.
INTRODUCTION
Today soil OM is becoming an important element for agricultural environment and
energy. Humic substances (HS), the major fraction of OM, are ubiquitous in the environment,
and have been documented to interact in some manner with over 50 elements from the periodic
table. The importance of HS in soil science and agriculture has been acknowledged for over 150
years, but scientists have encountered major challenges in understanding humic acid
functionalities.
Soil is a living system, in which the interaction of the various metabolic processes is
regulated in much the same way cellular processes are regulated: feedback inhibition; induction
of enzymatic activity; secretion and impact of pH; ionic strength; temperature; and the presence
and absence of inhibitors. Soil OM is composed of plant and animal debris in various stages of
decomposition by soil microorganisms. Humus is fully decomposed organic matter. Brown or
black in color, humus makes up 65-80 percent of the total organic matter in soil.
Humus-mineral complexes are components of the conglomerate soil colloids which
contain oxyhroxides and humus materials associated to present reactive seats of fertility in soils.
Due to its low specific weight and high surface area, humus has a profound effect upon the
physical properties of mineral soils with regard to improved soil structure, water intake and
reservoir capacity, ability to resist erosion, and the ability to hold chemical elements in a form
readily accessible to plants.
Humic substances (HS) are the product of humification, the biological process whereby
organic matter is converted into humic substances via transformation of plant lignin and cell
polyphenols by microbial synthesis in the soil. HS are composed of three major fractions: humic
acid (HA), fulvic acid (FA) and humin. Humic acids constitute the largest of the three fractions,
and are one of the most important constituents of fertile soils because of their profound direct
and indirect modes of action on soil chemical, physical, and biological properties.
Direct modes of action of HS on plant growth:
Effects on membranes resulting in improved transport of nutritional elements.
Enhanced protein synthesis.
Plant-hormone-like activity.
Enhanced photosynthesis.
Indirect Effects of HS on enzyme activity:
Solublization of microelements (e.g. Fe, Zn, Mn) and some macroelements (e.g.
K, Ca, P)
Reduction of active levels of toxic elements.
Enhancement of microbial populations.
Chemical-physical effects of HS on plant growth:
Combines soil particles in structural aggregates.
Favors the mineralization of the chemical substances which releases SO4, PO4,
NH4, NO3.
High exchange capacity.
Humin serves to stabilize soil organic matter by a) encapsulation of small polar
molecules (physical sequestration), b) binding of functionalized biomarkers (chemical
sequestration), and c) selective preservation of aliphatic biopolymers.
Figure 1. Stable Humus vs Productivity Figure 2. Clay-Organic Acid Nutrient Exchange
Sustainable cropping systems call for the protection of organic carbon (C), a major
component of HS. Over a one-year period, 32 to 98 percent of C in soil and plant residues is lost
as CO2. Results of various investigators concluded that 32 to 98 percent of soil humus present in
agricultural soils was in organo-mineral complexes. Pure culture studies have indicated that clays
may increase the efficiency of conversion of substrate C to biomass (Figure 3).
Figure 3. Clay-humic association via
Binding HS to clay by cationic bridges
Low levels (<2 percent) of elements that influence plant nutrition are one of the most
important constraints to crop growth. New technologies are needed for OM manipulation to
overcome current agronomic practices of organic matter (OM) maintenance in the soil. For over
17 years we established research trials in farmers’ fields in Western Idaho to scientifically
evaluate the efficacy of different humates products on crop yield and quality in potato
production. We evaluated over 30 different commercial humic substances derived from lignite
and leonardite. Collectively, the consistent use of good quality products in our replicated
research plots in different years resulted in a yield increase from 11.4 percent to the maximum of
22.3 percent.
METHODS
For each research trial, HA treatments were arranged in a randomized complete block
design,with four replications. HA treatments were applied as soil amendment, top-dressed, side-
dressed, or foliar, in accordance with standard commercial practices. For each top-dressed, side-
dressed, or foliar application, the hills were opened above the potato seeds for pre-emergence
treatments prior to application of the products. Liquid humic products were applied with solo-
pack sprayers to the opened furrow in accordance with manufacturers‘ recommendations.
Furrows were closed immediately after application of different commercial HA treatments. In
different trials, granular humates were weighed (40.48 kg.ha-1) and spread as evenly as possible
to treated rows according to block design randomizations. At the end of the crop season, potato
plots were harvested, graded, weighed, and quality parameters were evaluated. Data from these
years were subjected to analysis of variance of regression.
RESULTS AND DISCUSSION
Data from HA trials showed that different cropping systems responded differently to
different products in relation to yield and quality. Collectively, the consistent use of good quality
products in our replicated research plots in different years resulted in a yield increase from 11.4
percent to the maximum of 22.3 percent. Humic acid products enhanced nitrogen mineralization
in early season by an average of 9.6 percent. Research studies done by my colleagues, Drs. Jeff
Stark and Bryan Hopkins, reflect favorable findings regarding the impact of humics on yield and
quality (see Table 1). Over the past decade, there has been a major increase in the quality of
research and development of organic and humic acids by some well-established manufacturers.
Our experimentations with these commercial products showed an increase in the yield and
quality of crops (Figure 4).
Figure 4. Effects of Humic Acid Rate on Potato Yield
Table 1. Yield, specific gravity, petiole P and gross return in Russet Burbank
Potatoes under different rates of 10-34-0 Fertilizer
Bryan Hopkins and Jeff Stark, University of Idaho Aberdeen Research Station
O5
(kg/ha)
Humic
Acid
(L/ha)
Total US
No.1
>283g Sp.
gravity
Petiole P
(% dwt)
Gross
Return
(US$/ha)
0 0 394 225 146 1.077 0.24 4523
67.36 0 431 260 177 1.079 0.29 5110
67.36 14 444 279 186 1.080 0.31 5390
134.7 0 438 261 179 1.079 0.30 5187
134.7 28 446 278 193 1.079 0.32 5402
LSD @
1%
48 33 23 0.003 0.03
336
358
368
385 385
346
300
325
350
375
400
0 1 2 4 8 16
Yie
ld (
cw
t/acre
)
Humic acid (gal/acre)
Y = 343.4 + 12.01X-0.746X2
R2 = 0.92 ***
REFERENCES
Brady, N.C. 1974. The Nature and Properties of Soils, 8th Edn., MacMillan, New York, p. 137.
Chen Y. and T. Aviad. 1990. Effects of humic substances on plant growth. In: Humic
Substances in Soil and Crop Sciences: Selected Readings. MacCarthy, P. et al. (eds.). ASA-
CSSA, Madison, WI, p. 161.
Hendrix, P., et al. 1986. Detritus foodwebs in conventional and no-tillage agroecosystems.
BioScience, Vol.36:6, pp. 374-380.
Hopkins, Bryan and Jeff Stark. 2003. Humic Acid Effects on Potato Response to Phosphorus.
Presented at Idaho Potato Conference, January 22-23, 2003.
Ingham, E. et al. 1986. Trophic interactions and nutrient cycling in a semi-arid grassland soil. II:
system responses to removal of different groups of soil microbes or fauna. J. Applied Ecol.,
23, 615.
MacCarthy, P., et al.1990. An introduction to soil humic substances. P. MacCarthy, C.E. Clapp,
R.L. Malcolm and P.R. Bloom, Eds. In: Humic Substances in Soil and Crop Sciences:
Selected Readings. ASA-CSSA, Madison, WI, p. 1.
MacCarthy, P, P.R. Bloom, C.E. Clapp and R.L. Malcolm. 1990. In: Humic Substances in Soil
and Crop Sciences: Selected Readings, Soil Science Society of America, Madison, WI, p.
261.
Schnitzer, M. 1990. In: Humic Substances in Soil and Crop Sciences, ASA-CSSA, eds. P.
MacCarthy et al., Madison, WI, pp.65-89.
Schnitzer, M. 1986. In: Interactions of Soil Minerals with Natural Organics and Microbes, eds.
P.M. Huang and M. Schnitzer, SSSA Spec. Pub. No. 17, Madison, WI p. 87.
Seyedbagheri, Mir-M. and J.M. Torell. 2002. Field Studies of the Soil Foodweb and Nitrogen
Mineralization with Implications for Nutrient Management and Water Quality. Presented at
Research and Extension Regional Water Conference, 2002.
Stevenson, F.J. and X. –T. He. 1990. Nitrogen in Humic Substances as Related to Soil Fertility.
In: P. MacCarthy, C.E. Clapp, R.L. Malcolm and P.R. Bloom, Eds., Humic Substances
in Soil and Crop Sciences: Selected Readings, American Society of Agronomy, Madison,
WI, pp. 91-109.
Stieber, T., C. Shock, E. Feibert, M. Thornton, B. Brown, W. Cook, M. Seyedbagheri and D.
Westermann: 1994. Nitrogen Mineralization in Treasure Valley Soils, 1993 and 1994
Results, Malheur County Crop Research Annual Research Annual Report.
Westermann, D.and S.E. Crothers. 1980. Measuring Soil Nitrogen Mineralization Under Field
Conditions, American Society of Agronomy, Agron. J., 72:1009-1012.