Characterization of terrestrial dissolved organic matter fractionated by pH and polarity and their biological effects on plant growth
© Sleighter et al.; licensee Springer. 2015
Received: 30 November 2014
Accepted: 9 March 2015
Published: 10 April 2015
Humic substances are ubiquitous in the environment, complex mixtures, and known to be beneficial to plant growth. To better understand and identify components responsible for plant growth stimulation, a terrestrial aquatic DOM sample was fractionated according to pH and polarity, obtaining acid-soluble and acid-insoluble portions, as well as acid-soluble hydrophobic and hydrophilic fractions using C18. The various fractions were characterized then evaluated for their biological effects on plant growth using bioassays with corn at two carbon rates.
Approximately 43% and 57% of the carbon, and 31% and 69% of the iron, was found in the acid-insoluble and acid-soluble fractions, respectively. Upon separating the acid-soluble portion using C18 extraction, about 64% and 36% of the carbon (and 96% and 4% of the iron) was present in the hydrophilic and hydrophobic fractions, respectively. The acid-insoluble portion was more aromatic and less oxygenated than the acid-soluble fraction. The hydrophilic filtrate was oxygen-rich and contained mostly tannin-like molecules, while the hydrophobic retentate was more aromatic and lignin-like. During bioassay testing, it was found that more hydrophilic samples (those that are more oxygenated) yielded the highest response for shoot measurements. For root measurements, the lower DOC rate (0.01 mg/L C) gave better results than the higher DOC rate (0.1 mg/L C). Also, the hydrophobic, less oxygenated acid-insoluble sample performed better than the more hydrophilic acid-soluble portion. The polarity fractions at the lower carbon application showed that larger root systems occurred when there was more hydrophobic C18 retentate material present. The opposite was true for the root system at the higher carbon application, where larger roots existed when more hydrophilic C18 filtrate material was present.
Compositional differences were found when comparing the acid-soluble versus acid-insoluble portions and the hydrophobic versus hydrophilic C18 fractions, and activity with respect to plant stimulation was discerned. While a carbon rate affect was observed during foliar application to corn plants (with the lower carbon rate generally yielding the best biological stimulation), the various observed trends indicate that plant response is due to not only the amount of carbon present but also the type of carbon.
Humic substances, which are ubiquitous in the environment, are present in varying amounts in all natural waters, soils, and sediments [1-3]. They are complex mixtures, containing thousands of individual molecules, all varying in their individual structure, function, reactivity, and polarity. Humic substances have long been regarded as beneficial to soil fertility and plant growth, and there are multiple excellent reviews on the subject that encompass decades of studies [4-6]. The positive outcomes are likely a combination of both direct and indirect effects, and humic substances have been shown to suppress the effect of pathogens and fungi, enhance lateral root development and root length/density, increase the cation exchange capacity and pH buffering capacity of soils, increase the availability and uptake of micronutrients, and promote growth and development via a hormone-like mechanism [7-13]. While there are many studies that have demonstrated improved plant health by treatment with humic substances, several questions remain, such as the best way to treat plants (seed vs. soil vs. foliar application), the rate/amount for treatment, and when to perform application(s), among numerous others. Because there are so many variables associated with the treatments on an agricultural level, there are sometimes conflicting and controversial results. It is likely that the optimal method and quantity for treatment varies depending on the crop, soil properties, and environmental conditions, as the mechanism for enhanced plant growth is uncertain.
Extensive chemical characterization of humic substances, and dissolved organic matter (DOM) in general, by use of advanced analytical techniques  has increased our understanding of the sources and composition of these complex mixtures. While numerous studies have highlighted the ability of humic substances (in general) to enhance plant response and growth parameters, the new challenge is to ascertain what portion or specific component(s) of the humic substances is most responsible for generating the positive response . Nardi et al.  found that the lowest molecular weight portion of a humic acid fractionated by size exclusion chromatography was most active in stimulating plant metabolism, and this fraction was the most hydrophilic, containing more carbohydrates and less lignin-derived material, when compared to the larger size fractions. Other studies also found a link between hydrophobicity and plant response, but the more hydrophobic humic acids were those most active in plant response, with some humics acids increasing root length while others increased root density [17,18]. It is not uncommon for studies to present conflicting findings, especially when the various studies perform applications of the humic substances in different ways to different plants under different growing conditions, and also varying in concentration. It is clear that further research is needed to better understand the effects of humic substances on plants, especially as the use of humic substances for agricultural purposes is becoming more widely accepted and promoted.
Here, a terrestrial aquatic DOM sample was fractionated according to pH solubility and then polarity. The whole, original sample is available commercially from FBSciences, Inc. and has been shown to yield positive plant growth responses when utilized in agricultural applications. However, there is a need to identify what fractions of this DOM are most responsible for plant responses, so that we may employ further refinements to isolate and make available a more effective product. Thus, the whole sample was acidified to obtain the acid-insoluble and acid-soluble portions (similar to the method used by the International Humic Substances Society, ), and then, the acid-soluble portion was fractionated further into polar and non-polar fractions using C18 solid phase extraction (simulating that which occurs during reversed phase liquid chromatography, [20-22]). Material that passes through the C18 is polar, hydrophilic, and is referred to as the filtrate, while the material that is retained by the C18 (i.e., the retentate) is non-polar and hydrophobic . The various fractions were chemically characterized using an array of advanced analytical techniques. Ultraviolet visible (UV/Vis) absorbance spectroscopy and excitation emission matrix spectroscopy (EEMs) were utilized to understand the optical properties of the chromophoric and fluorescent DOM [24,25]. To understand bulk chemical functionalities, liquid-state proton nuclear magnetic resonance (1H NMR) spectroscopy was employed . Finally, to obtain molecular-level information, electrospray ionization Fourier transform ion cyclotron resonance mass spectrometry (ESI-FTICR-MS) was used [27-29]. After characterization, the original whole and fractionated samples were subjected to plant bioassays at two carbon concentrations. Bioassays (performed in vivo) are utilized as a tool for measuring the effects of the different sample types on plant activity, in an effort to correlate molecular level details with plant response (i.e., root and shoot elongation, fresh and dry weights).
The two main goals of this study were to 1) chemically characterize the composition of the DOM fractionated according to pH solubility and polarity using a variety of advanced analytical techniques, and 2) demonstrate statistically significant responses upon treating plants with the fractionated samples in comparison to a control, in order to examine the influence that fractionation of the NOM has on plant growth and biological response.
In this study, a terrestrial aquatic DOM sample was utilized for fractionation into various components. The source of the DOM is from fresh water in Northern Europe, and the final DOM product has been concentrated by a proprietary method and is commercially available from FBSciences, Inc. The “whole” sample was acidified drop-wise with 12 M HCl (trace metal grade, Fisher Scientific) to pH < 2. Precipitation was allowed to occur at room temperature for 40 hours. The sample was centrifuged to isolate the solid “acid-insoluble” portion from the liquid “acid-soluble” portion. The “acid-insoluble” solids were rinsed with acidified ultrahigh quality (UHQ) water and freeze-dried to obtain a dry powder. The “acid-soluble” portion was fractionated further using C18 solid phase extraction (SPE, ), to obtain the hydrophobic retentate portion (i.e., what is retained by the C18 resin) and the hydrophilic filtrate portion (i.e., that which passes through the C18 resin). The C18 extraction disk (3 M Empore) was cleaned and activated using methanol (LC-MS grade, Fisher Scientific) and acidified UHQ water. The “acid-soluble” sample was passed through the C18 disk at a flow rate <25 mL/min, and the solution that passed through the resin was collected as the “filtrate”. That which was adsorbed onto the resin was rinsed with acidified UHQ water and eluted off the resin with LC-MS grade methanol, to give the “retentate” portion.
Dissolved organic carbon (DOC) and Iron (Fe) Analysis
The C18 filtrate and retentate samples were rotary evaporated to remove methanol and replaced with UHQ water. The dried acid-insoluble fraction was re-dissolved in water amended with ammonium hydroxide (NH4OH, final concentration 0.05%, pH 9). All fractions were then analyzed for their dissolved organic carbon (DOC) and iron (Fe) concentrations. Samples were analyzed for their DOC concentrations by high temperature catalytic combustion to CO2 on a Shimadzu TOC-VCSN total organic carbon analyzer calibrated with potassium hydrogen phthalate (Shimadzu). Samples were analyzed for their Fe content on a Perkin Elmer AAnalyst 200 Atomic Absorption Spectrometer calibrated with an iron reference standard solution (Fisher Scientific).
UV/Vis and EEMs Analysis
UV/Vis absorbance values were measured simultaneously as EEMs spectra were acquired on a Horiba Scientific Aqualog spectrophotometer with an excitation range of 240–600 nm at 3 nm intervals and an emission range of 213–623 at 3.368 nm intervals, with an integration time of 1 sec. All samples were analyzed at a range of DOC values (approximately 0.5-8 mg/L C), and acquired spectra were corrected for their inner filter effects and Rayleigh masking using the Aqualog V3.6 software, which was also utilized for area integrations. Humic-like peaks A and C were integrated at [Ex 240–300 nm; Em 400–500 nm] and [Ex 300–360 nm; Em 400–500 nm], respectively, while peptide-like peak T was integrated at [Ex 240–300 nm; Em 250–350 nm] . Specific UV absorption at 254 nm (SUVA254) was calculated based on the absorbance at 254 nm and the DOC concentration , and the fluorescence index (FI) was calculated from the ratio of emission intensity at 470:520 nm at excitation 370 nm [24,32].
Cation Exchange Resin Procedure
Because these samples contained a significant amount of Fe, cation exchange resin was utilized to prepare the samples for NMR and FTICR-MS, as these analyses are known to be hindered by the presence of paramagnetic species and ionic salts, respectively. The whole, acid-soluble fraction, and C18 filtrate were prepared using cation exchange resin (AG MP-50 resin, hydrogen form, 100–200 dry mesh size, Bio-Rad), similar to the guidelines established by the International Humic Substances Society . The samples were prepared in batches, according to manufacturer guidelines, where the sample was added directly to the cleaned resin, stirred for 60 minutes, and then centrifuged to remove the resin from the sample. Using 3 steps of resin addition, 80-90% of the Fe was removed. It was not necessary to use the cation exchange resin on the acid-insoluble or C18 retentate samples, as these samples contained significantly less Fe.
The liquid-state 1H NMR spectra were obtained on a 400 MHz Bruker Biospin Avance III NMR equipped with a broadband inverse probe using a water suppression pulse program (optimized WATERGATE pulse sequence ). This sequence suppresses the large peak due to water protons (at 4.7 ppm), allowing for the detection of protons from the natural DOM that would otherwise be obscured. This program also eliminates pre-concentration and re-dissolution steps that potentially lose an unknown portion of the DOM. The acid-insoluble sample was re-dissolved using sodium deuteroxide in D2O diluted to pH 9 with UHQ water. All samples had a final sample composition of 90:10 H2O:D2O. Spectra were acquired with a 1 msec recycle delay and a time domain of 16 k, with 1000 scans (giving an approximate 1 hour analysis time). The scans were co-added and the summed free induction decay (FID) signal was exponentially multiplied and zero-filled once. The spectra were processed with a line broadening of 10 Hz.
For both NMR and FTICR-MS, the C18 filtrate and retentate samples were analyzed together in filtrate: retentate ratios of 100:0, 75:25, 50:50, 25:75, and 100:0. These ratios were also used during bioassays (described in detail below), in order to better understand how differing ratios of these two very different fractional components can influence plant response.
The samples prepared with cation exchange resin, described in the NMR section above, were also utilized for FTICR-MS analysis. The acid-insoluble sample was re-dissolved using UHQ water amended with NH4OH (final concentration 0.05%, pH 9). All samples were diluted to give a final sample composition of 1:1 H2O:MeOH and were continuously infused into an Apollo II ESI ion source (operating in negative ion mode) of a Bruker Daltonics 12 Tesla Apex Qe FTICR-MS using a syringe pump operating at 120 μL/hr. ESI voltages were optimized for each analysis using a spray shield voltage of 3.3-3.5 kV and a capillary voltage of 4.0-4.2 kV, yielding consistent and stable ESI spray shield and capillary currents of 180–210 nA and 20–30 nA, respectively. Ions were accumulated for 2–5 sec in a hexapole before being transferred to the ICR cell, where 300 transients, collected with a 4 MWord time domain, were added, giving about a 30–40 min total analysis time. The summed FID signal was zero-filled once and Sine-Bell apodized prior to fast Fourier transformation and magnitude calculation using the Bruker Daltonics Data Analysissoftware.
Prior to data analysis, all samples were externally calibrated with a polyethylene glycol standard and internally calibrated with fatty acids, dicarboxylic acids, and other naturally present compounds that are part of various CH2 homologous series . All m/z lists, created using a signal to noise threshold of 3, were exported for further analysis. Mass spectra were found to be reproducible, and the various samples were significantly different from one another when compared to instrumental duplicates of the same sample . A molecular formula calculator generated empirical formula matches for all samples using carbon, hydrogen, oxygen, nitrogen, and sulfur with atomic ranges of C5-50H5-100O1-30N0-1S0-1. Molecular formulae were assigned based on previously described rules , and the calculated theoretical m/z values of the assigned formulae agreed with measured m/z values with an error value of ≤ 0.5 ppm. For all samples, 82-92% of all peaks were assigned a unique molecular formula (excluding contributions from 13C isotopes), and these formulae accounted for 91-97% of the summed total spectral peak magnitude. From the molecular formula assignments, average (by number and magnitude-weighted) mass spectral characteristics were calculated .
In order to reveal the subtle differences among the NMR spectra and, separately, among the formulae assigned to FTICR-MS data, principal component analysis (PCA) was utilized. PCA, which assumes a linear relationship, reduces a multidimensional space into fewer dimensions, where the first dimension (i.e., the first principal component, PC1) explains the most variance. The second dimension (PC2), which is orthogonal to the first, explains most of the residual variance. The PCA output gives scores and loadings, which represent the projections of the samples and the variables, respectively, onto each PC. The loadings indicate that variable’s contribution to the data variability along each PC. From these results, the samples and variables can be plotted on a two-dimensional PCA projection (a biplot), not only to group the samples according to their differences, but also to determine relationships between samples and variables. Data was compiled to create NMR and FTICR-MS matrices for each PCA.
The intensity values for the NMR spectra at 0.5-11 ppm were exported for each sample from the instrument at the resolution that the NMR measures, giving intensity values approximately every 0.0008 ppm, yielding 13,225 data points per sample. Because this level of resolution unnecessarily generates an excessively large dataset, an in-house written MatLab code was utilized to average across every 5 data points, giving a new resolution of 0.004 ppm and 2645 data points per sample. Data were normalized for each sample so that the summed total intensity equaled 1 for all samples.
For the FTICR-MS PCA, a data matrix was created for the samples and the complete set of unique CHO-only formulae using the relative magnitudes of the peaks. Relative magnitude is simply calculated by dividing the peak magnitude by the summed total peak magnitude for each sample. If a formula was not detected in that sample, a 0 was given in the matrix. Data were normalized for each sample so that the summed total magnitude equaled 1 for all samples, and PCA was conducted according to a previously published method .
Whole and fractionated samples were tested for plant response using a foliar application on corn (Zea mays L.) seeds treated with a pesticide package (to give healthy, pathogen-free seeds). Planting pots (18 cm diameter) filled with a vermiculite (grade 2, ULINE) substrate media were used, and 8 seeds were planted per pot. There were 3 replicate pots per treatment (including the control). Emergence was allowed to progress for 6 days, and then seedlings were thinned (to allow more space for root growth), from 24 to 10 seedlings per treatment. The seedlings continued to grow for another 8 days, and then the foliar treatment was applied. The DOC concentrations of all 8 samples (whole, acid-insoluble, acid-soluble, and the 5 filtrate : retentate ratios of 100:0, 75:25, 50:50, 25:75, and 0:100) were normalized, and then 2 DOC rates were used for the foliar application: 0.01 and 0.1 mg/L C (UHQ water was used for the control). By using the same number of sprays from a hand sprayer containing the specified DOC value of each sample, 7 mL of each sample at each concentration were sprayed onto the plant foliage of each pot, ensuring adequate and uniform coverage of the plant leaves without inducing dripping or runoff of the product from the leaf margins. The plants continued to grow for another 7 days, and then the plants were harvested to evaluate their response to the treatment. Previous experiments (data not shown) have indicated that 7 days is the optimal amount of time post foliar application for this pot size. This time frame is long enough for the root system to grow and respond without the occurrence of root knotting but not so long that the plants become stressed due to the lack of macronutrients.
The entire growing period occurred in a greenhouse during the summer of 2014, where watering occurred on a daily basis. The following day/night program was used: day from 7 AM at 21–25°C with 50-60% humidity; night from 7 PM at 16–18°C with 50-60% humidity. Plants were not watered the day prior to harvesting, to allow the substrate media to partially dry. The plants were extracted from the substrate, the roots were carefully washed to remove the vermiculite, and then fresh weight biomasses (for all seedlings of all replicates for each treatment taken together) were recorded. Then, the longest root and shoot of each individual seedling (for each replicate and each treatment) were measured to evaluate root and shoot elongation. The seedlings were then allowed to dry overnight in an oven at 60°C on aluminum foil, prior to taking dry masses of the full root and the full shoot systems for each seedling individually.
The assessment parameters were statistically evaluated by ANOVA single factor and Duncan’s multiple range tests, to determine if each treatment is statistically different than the control and if the treatments are statistically different from one another, respectively. A value of P = 0.05 was chosen to determine the significance of the data (if P > 0.05 the data are not statistically different; if P ≤ 0.05 the data are statistically different).
Results and Discussion
Carbon and Iron Concentrations
Characterization from Optical Measurements
Calculations from optical measurements of each sample
EEMs Peak Areas
(L mg −1 m −1 )
Table 1 also gives the FI values, along with the percentages that humic-like peak A, humic-like peak C, and peptide-like peak T contribute to the total integrated fluorescence (for the samples analyzed at approximately 5 mg/L C). Higher SUVA254 and lower FI values are both indicators of aromaticity, with SUVA254 being indirectly proportional to FI. They are calculated from different parameters (SUVA254 using low wavelength adsorption and DOC concentration; FI using a ratio of higher wavelength fluorescence and is independent of DOC) and are often evaluated together, because FI is not subject to the same interferences as SUVA254 (e.g., Fe concentration). While Fe is known to quench fluorescence , FI is rarely affected by Fe concentrations because it is calculated by a ratio of emissions whose signals are decreased in the same manner. Corresponding with the SUVA254 values, the acid-insoluble portion has a lower FI than the acid-soluble sample, and the C18 retentate has a lower FI than the filtrate. While the whole sample had the highest SUVA254, its FI falls between the acid-insoluble and acid-soluble. The whole sample has the highest Fe concentration, inflating its SUVA254 value more severely than the other samples. However, in this case based on our results, FI seems to reveal the true trend of aromaticity amongst the fractionated samples, better than SUVA254.
Figure 2c gives the integrated Peak A areas from the EEMs analyses across the DOC range for all samples, while Figures 2d-f show the EEMs spectra for the whole, acid-insoluble, and acid-soluble samples. The whole and acid-soluble samples give quite similar EEMs spectra (which are also comparable to the hydrophobic retentate and hydrophilic filtrate samples whose spectra are not shown). The acid-insoluble sample appears to be somewhat different, with a wider (in the emission dimension) peak A (Ex 240–300 nm, Em 400–500 nm) and a less well defined peak C (Ex 300–360 nm, Em 400–500 nm). The hydrophobic retentate has the highest fluorescence, followed by the acid-soluble sample that fluoresces similarly to the whole sample, and the hydrophilic filtrate sample fluoresces slightly less than those. The acid-insoluble sample has the lowest fluorescence, but that is likely due to the fluorescence intensity of peak A being more widespread in this sample than in the others. As discussed above, Fe is known to increase absorbance values at low wavelengths as well as quench overall fluorescence . This is likely why the hydrophobic retentate, that contains very little iron (Figure 1), has the highest fluorescence. The percentages that peaks A and C contribute to the total fluorescence are quite similar for all samples, with peak C being about 2/3 of that of peak A. Peak T (Ex 240–300 nm, Em 250–350 nm) is very low for all samples, as expected based on the terrestrial nature of these samples. This is consistent with the low FI values, which also indicate that there is little influence from microbial DOM.
Characterization from Proton NMR Measurements
Proton NMR peak area integrations at the given ppm ranges, for each sample
C = C-H
O = C-H
C18 Fil:Ret 100:0
C18 Fil:Ret 75:25
C18 Fil:Ret 50:50
C18 Fil:Ret 25:75
C18 Fil:Ret 0:100
Based on the NMR spectra and area integrations, the acid-soluble sample is more oxygenated (2–5 ppm), whereas the acid-insoluble portion contains more olefins and aromatics (5–9 ppm). For the C18 samples, as the ratio of filtrate : retentate goes from 100:0 to 0:100, the aliphatic and aromatic components both increase, while the oxygenation decreases. While there is much overlap of the samples across the entire chemical shift range, the subtle differences amongst the spectra are revealed by utilizing PCA.
The original PCA executed on the NMR data revealed that statistical differences were primarily driven by the pH affect. Acidic samples were enriched in acetic acid and formic acid, while neutral/basic samples were enriched in acetate and formate. The presence or absence of methanol was also driving the PCA (particularly for the C18 samples). Because these small molecules exist as sharp peaks in the spectra, they are the first (and largest) differences found by PCA. Thus, a data matrix was created for a new PCA, ignoring certain regions of the NMR spectra. The following areas were deleted: >8 ppm, 3.2-4 ppm, and 1.8-2.4 ppm, to remove the areas of the spectrum that depend on pH, as well as the methanol peak. The subsequent NMR PCA matrix had a dimension of 8 (samples) x 1537 (NMR intensity values as variables).
The reconstructed NMR spectra elucidate the reasons for the sample groupings. From the PC1 loadings (Figure 4b), it is clear that the large aliphatic peak at about 1.5 ppm versus the oxygenated region at 2.4-3.2 ppm are the main factors driving the PC1 variance. Because the peak at 1.5 ppm has a negative PC1 loading, it is enhanced in the whole, acid-insoluble, and acid-soluble samples (as they have negative PC1 scores). The whole and acid-insoluble samples are more enriched in the peak at 1.5 ppm than in the oxygenated region (as they have larger negative PC1 scores). However, the acid-soluble sample has both of these regions at quite high intensities, giving a PC1 score that is closer to 0 (but still negative). The peak at 1.2 ppm (which is defined in all samples, Figure 3) is due to CHx protons on aliphatic chains, while the peak at 1.5 is likely due to aliphatic protons that are attached to carbons that are next to either an olefin group or a carboxyl group (H2C = CH-CH2-R; HOOC-CH 2 - CH2-R). It is clear that this aliphatic peak at 1.5 ppm is more prevalent in the samples fractionated by pH and less so in the C18 samples (Figure 3). Because this peak is prevalent in the acid-soluble sample, we would also expect to detect it in the polarity-separated samples. It is likely that this region is less defined in the C18 samples, because these types of functionalities partition between the hydrophobic retentate and hydrophilic filtrate depending on the composition of the R group. The presence of a well-defined peak at 1.5 ppm in the acid-soluble sample and the lack there of in the C18 samples leads to their separation in the PC1 dimension.
The C18 samples (with positive PC1 scores) are more enriched in the oxygenated region at 2.4-3.2 ppm (as this region has positive PC1 loadings) than in the peak at 1.5 ppm. Furthermore, the oxygenation degree increases as more of the filtrate sample is present in the mixed ratios of C18 filtrate : retentate. These observations are in agreement with the expected mechanism of the extractions, where polar species (i.e., those that are more oxygenated) are not adsorbed to the resin and thus remain in the filtrate portion. However, the C18 samples do not simply increase horizontally in the PC1 dimension, but rather on a diagonal, meaning that their differences are a combination of PC1 and PC2 variance.
In the PC2 dimension, the main drivers of the variance (Figure 4c) are the peak at 1.5 ppm and the oxygenated region at 2.4-3.2 ppm versus the aromatic region at 7–8 ppm and the aliphatic region at 0.5-1.2 ppm. The acid-insoluble sample has a very low PC2 score, indicating that it is particularly enriched in the aromatic region, as well as aliphatic CHx functionalities. The other samples are more oxygenated (Figure 3, Table 2), giving higher PC2 scores. The samples with higher C18 filtrate portions having higher PC2 scores are more enriched in the oxygenated area, while the C18 retentate-dominated samples with lower PC2 scores are enriched in the aromatic and CHx aliphatic (0.5-1.2 ppm) areas. In this PC2 dimension, the acid-soluble sample score falls between the 50:50 and 75:25 filtrate : retentate ratio sample scores, as expected based on the relative proportions of the filtrate and retentate in the original acid-soluble sample (Figure 1).
Characterization from FTICR-MS Measurements
Average (by number and magnitude-weighted) mass spectral characteristics for each sample
C18 Fil:Ret 100:0
C18 Fil:Ret 75:25
C18 Fil:Ret 50:50
C18 Fil:Ret 25:75
C18 Fil:Ret 0:100
The whole and acid-soluble samples are very similar with regard to their averaged elemental ratios and heteroatom composition, with the acid-insoluble material containing the highest amount of CHO-only formulae, indicating that the heteroatoms are less likely to precipitate, especially sulfur-containing components (Table 3). The C18 filtrate contains more heteroatoms than the C18 retentate (which is consistent with previous studies [23,30,36], as these polar species are not adsorbed to the C18 resin, especially the sulfur species (which are typically also associated with high oxygenation, such as sulfates, and are very polar). Also in Table 3 are the number-averaged and magnitude-weighted calculations. Again, the whole and acid-soluble samples are quite similar. The acid-insoluble sample has a much lower O/C average and an H/C average that is slightly higher than the whole and acid-soluble samples. These values indicate that the precipitated acid-insoluble material contains components with very little oxygenation. As the sample progresses from filtrate to retentate, the average O/C and DBE/C ratios decrease. This indicates that the filtrate is more oxygenated and less aromatic than the retentate portion. These averaged mass spectral characteristics agree quite well with the optical and NMR results.
Mass spectral characteristics of the formulae responsible for the variance in the FTICR-MS PCA dataset
General characteristics of molecular formulae from PCA
Purple (enriched in filtrate-dominated samples)
Green (enriched in retentate-dominated samples)
Red (enriched in acid insoluble)
Bioassays and Plant Response
Results of the bioassays employing foliar applications of the 8 samples at 2 carbon rates
Fresh weight (g)
Dry Weight (mg)
32.7 ± 3.5
28.2 ± 3.9
155 ± 19
95 ± 36
Whole, 0.01 mg/L C
33.0 ± 3.6
32.6 ± 4.3
165 ± 31
118 ± 23
Acid soluble, 0.01 mg/L C
36.2 ± 5.5
34.1 ± 3.4
189 ± 25
125 ± 35
Acid insoluble, 0.01 mg/L C
36.4 ± 8.0
27.8 ± 3.2
221 ± 37
108 ± 25
100:0 Filt : Ret, 0.01 mg/L C
37.0 ± 3.3
30.6 ± 3.9
184 ± 20
111 ± 32
75:25 Filt : Ret, 0.01 mg/L C
35.5 ± 5.6
27.9 ± 6.4
192 ± 53
89 ± 36
50:50 Filt : Ret, 0.01 ppm
38.3 ± 4.4
27.5 ± 3.6
219 ± 21
92 ± 21
25:75 Filt : Ret, 0.01 mg/L C
38.8 ± 5.5
26.3 ± 3.3
221 ± 39
84 ± 20
0:100 Filt : Ret, 0.01 mg/L C
36.4 ± 3.1
27.0 ± 3.5
231 ± 24
98 ± 25
Whole, 0.1 mg/L C
33.0 ± 1.9
32.1 ± 4.1
160 ± 14
112 ± 28
Acid soluble, 0.1 mg/L C
35.5 ± 5.5
31.1 ± 2.5
173 ± 25
112 ± 23
Acid insoluble, 0.1 mg/L C
36.6 ± 5.6
29.1 ± 4.4
204 ± 30
113 ± 39
100:0 Filt : Ret, 0.1 mg/L C
32.0 ± 3.5
29.2 ± 5.0
229 ± 40
118 ± 36
75:25 Filt : Ret, 0.1 mg/L C
31.9 ± 3.7
26.5 ± 4.1
214 ± 31
98 ± 29
50:50 Filt : Ret, 0.1 mg/L C
37.2 ± 5.5
26.8 ± 4.0
214 ± 37
90 ± 22
25:75 Filt : Ret, 0.1 mg/L C
33.2 ± 3.8
27.9 ± 4.4
195 ± 61
105 ± 33
0:100 Filt : Ret, 0.1 mg/L C
31.7 ± 5.6
26.3 ± 3.5
202 ± 45
90 ± 23
In general, the lower DOC rate (0.01 mg/L C) gave higher root elongation values, in comparison to the higher DOC rate of 0.1 mg/L C (Table 5, Figure 7). The whole, acid-soluble, and acid-insoluble samples all gave root elongation values higher than the control for both DOC rates, but none were statistically better. For the C18 fractionation samples, the 50:50 and 25:75 mixtures of the filtrate : retentate gave the highest root elongations. In regard to dry root mass, the whole sample was better, but not statistically, than the control for both DOC treatments, but the acid-soluble and acid-insoluble gave root masses that were statistically better (more so for the lower DOC rate). In this case, the acid-insoluble portion that is more hydrophobic gave the best results for the samples fractionated by pH. However, the samples fractionated by polarity display the most interesting trends for the dry root mass measurements of the bioassay. At the lower DOC rate of 0.01 mg/L C, the root masses increased as the C18 mixed samples became dominated by the hydrophobic retentate. The 100:0 filtrate : retentate sample had higher dry root mass than the control (but not statistically better), while the other 4 samples (75:25, 50:50, 25:75, 0:100 filtrate : retentate) were all statistically better and increased in that order. The opposite is true for the higher DOC rate of 0.1 mg/L C, where root mass increased as the samples became dominated by the hydrophilic filtrate. In this case, all 5 mixed samples gave root masses statistically better than the control, but the order here was reversed, where 100:0 filtrate : retentate yielded the highest root mass. It should also be noted that while all of the C18 fractionation samples gave positive results for dry root mass, they largely gave lower dry shoot masses than the control (but not statistically worse), except for the 100:0 filtrate : retentate sample that gave higher dry shoot masses than the control. It is evident that the application was taken up easily by the foliage and that it impacted the root system most.
The results presented here are a good example highlighting that plant response is due to not only the amount of carbon applied but also the type (i.e., fraction) of carbon. Certain parts of the plant (root vs. shoot) appear to respond differently to various types of carbon (hydrophilic vs. hydrophobic). These types of contradictory effects have also been reported in other studies [6,15-18]. While the focus for this foliar application was on the amount and type of carbon, it is likely that the trace metals and other micronutrients naturally present in the DOM also play an active role in enhancing plant growth [46-48]. In some cases, the hydrophilic samples (i.e., the acid-soluble or filtrate-dominated samples) gave the best plant response (i.e., shoot elongation and dry shoot mass at both DOC rates, dry root mass for the filtrate-dominated samples at the higher DOC rate of 0.1 mg/L C). These hydrophilic samples also have the highest Fe content. Other times the hydrophobic samples (i.e., the acid-insoluble or retentate-dominated samples) were better (i.e., dry root mass, especially for the retentate dominated samples at the lower DOC rate of 0.01 mg/L C). The acid-insoluble portion contains less Fe than the acid-soluble sample, but still has a significant Fe concentration, whereas the hydrophobic C18 retentate is nearly void of Fe. In general, the hydrophobic samples have lower Fe contents. It has yet to be determined whether these plant responses are due to the type of carbon components in each of these fractions (i.e., hydrophilic polar vs. hydrophobic non-polar) or due to the varying concentrations of Fe and other micronutrients that are also present. While more research is necessary to discern the mechanism(s) responsible for these observations, this study is an example of enhanced plant growth during controlled application of humic substances that vary in their chemical components and concentrations. Future studies that alter the DOC and micronutrient rates in a systematic manner will provide an enhanced understanding of this likely synergistic plant stimulation. Moreover, the application method (foliar in this case) may play a key role in determining the plant responses. Thus, other types of applications (such as seed treatment and soil application) are also being investigated.
The acid-insoluble component accounted for 43% of the carbon and 31% of the iron of the whole sample. After extraction of the acid-soluble portion, the C18 retentate portion contained 36% and 4% of the carbon and iron, respectively, while the remaining (and majority of) carbon and iron was found in the filtrate portion. The whole and acid-soluble samples were very similar, as characterized by NMR and FTICR-MS. The acid-insoluble sample was very low in oxygen and was mostly aromatic, but still contained a significant portion of aliphatics. A clear shift in the chemical composition was observed for the C18 samples, where the filtrate and retentate samples were mixed at ratios of filtrate : retentate 100:0, 75:25, 50:50, 25:75, and 0:100. As more retentate was added, the O/C ratios decreased while the DBE increased (with H/C not changing significantly). The tannin-like component dominates the filtrate portion, while the lignin-like component dominates the retentate portion, due to the differences in their polarity and hydrophobicity. PCA assisted in revealing the more subtle differences between the whole sample fractionated according to pH, as well as the acid-soluble portion fractionated using C18 resin to obtain the filtrate and retentate samples.
Bioassays using foliar applications of the 8 samples at 0.01 and 0.1 mg/L C demonstrated that plant responses are not only due to the amount of carbon but also due to the type of carbon present. Samples of a more hydrophilic nature (those that are most oxygenated as revealed by the NMR and FTICR-MS analysis) yielded the highest response for the shoot measurements. However, the root measurements were more responsive than the shoot. The lower DOC rate of 0.01 mg/L C in general gave higher root elongation values than the higher DOC rate of 0.1 mg/L C. The acid-insoluble and acid-soluble portions individually gave higher root elongation and larger root masses than the whole sample and the control, with the hydrophobic, less oxygenated acid-insoluble sample performing better. Based on dry root masses, the C18 polarity fractions showed that larger root systems occurred when there was more hydrophobic material present at the lower carbon application (0.01 mg/L C). The opposite was true for the root system at the higher carbon application (0.1 mg/L C), where larger roots existed when more hydrophilic material was present. This study clearly demonstrates that plant growth can be improved by the controlled application of humic substances that vary in their chemical components and concentrations. However, mechanisms for these enhancements remain unclear. Further work is necessary to discern whether the DOC type and concentration are responsible for the improved plant growth or whether micronutrients are more significant, but it is likely a combined effect in which both variables are important.
We thank the College of Sciences Major Instrumentation Cluster at Old Dominion University for their assistance with NMR and FTICR-MS data acquisition. We also thank the two anonymous reviewers and editor Dr. Marios Drosos whose comments significantly improved the quality of this manuscript.
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