# Evidence, Regulation, and Consequences of Nitrogen-Driven Nutrient Demand by Turfgrass

Authors: Wayne R. Kussow; Douglas J. Soldat; William C. Kreuser; Steven M. Houlihan
Journal: ISRN Agronomy
 (2012)

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## Abstract

Nutrient uptake is strongly influenced by plant growth rate. Accelerated growth leads to nutrient levels incapable of sustaining the optimal growth rate, resulting in shoot to root signaling for increased nutrient absorption. The factors controlling nutrient demand in turfgrass and its consequences have not been investigated. The objectives of this research were to verify that turfgrass exhibits the principal characteristics of demand-driven nutrient uptake and to identify the primary factor controlling nutrient demand via regulation of growth rates. Kentucky bluegrass clipping production increased linearly up to annual fertilizer N rates of 600 kg ha−1 and to 1000 kg N ha−1 for creeping bentgrass. At the typical annual N fertilization rates of 150 to 300 kg ha−1 for the two grasses, N supply was the primary determinant of turfgrass growth rate, plant nutrient demand, and nutrient uptake. Nitrogen uptake accounted for over 88% of uptake of all other nutrients. Uptake of P and K were strongly related to tissue N content irrespective of soil test levels. Variations in turfgrass species and cultivar nutrient requirements and nutrient use efficiencies were found to be directly related to differences in growth rates and, by inference, to differences in nutrient demand.


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## Body

## 1. Introduction

Nutrient demand is well established as having strong control over plant responses to varying external nutrient supplies [1–4]. Nye and Tinker [5] were among the first to articulate a definition of nutrient demand. Drawing from the pioneering research of Williams [6] and subsequent work by Clarkson [7], Lonergan and Asher [8] Nassery [9], Pitman [10], and White [11, 12], they defined nutrient demand as a plant property directly arising from changes in plant weight and composition that is expressed at root surfaces and relies on strong feedback control of root activity by the rest of the plant, possibly triggered by changes in the amounts of cytosol carbohydrates and inorganic nutrients in the root or shoot.Details of how plant shoot growth triggers expression of nutrient demand in roots are being intensively researched. White [12] hypothesized that the influx of P into root cortical cells is regulated by the turnover rate of inorganic P in the cytoplasm and the rate of transport to shoots. Cooper and Clarkson [13] and Marschner et al. [14] have confirmed the rapid xylem-phloem cycling and recycling of nutrient ions and certain metabolites in plants, thereby lending credence to White’s [12] hypothesis. This rapid cycling and recycling of nutrient ions and metabolites has become accepted as the basic means whereby shoot to root signaling of whole plant nutrient status is achieved and leads to integration of root membrane nutrient absorption rates with whole plant nutrient demand [13].Activation of ion uptake by roots is thought to result from the influences of fluctuations in cytosol contents of nutrient ions or metabolic products such as glutamine [15] or glutathione [16] on the functioning of one or more of the three classes of ion transporters—channels, pumps and receptors—all residing in root cell membranes. Suggested means whereby this occurs include energization of transport proteins by electrochemical proton gradients [17] or transducing molecules [16], the switching of gated ion transport channels [18] and cotransport to maintain cytosol charge balance [19, 20].The level or intensity of plant demand for a nutrient is directly proportional to the difference between its plant tissue nutrient content at any given moment and that required to sustain an optimal growth rate [15]. Hence, unsatisfied nutrient demand in a plant is very high when the external nutrient supply is far below that enabling the plant to meet its physiological requirements but approaches zero as nutrient supply becomes sufficient to meet the demand established by the current rate of plant growth [12]. When unsatisfied nutrient demand exists, nutrient uptake rate is more closely related to plant growth rate than external nutrient concentration and indirectly determines uptake from a given level of external supply [1–3]. Once external nutrient supplies are sufficient to meet plant demand, long-term uptake and tissue nutrient content typically remain constant with further increases in the external supplies [21]. When external nutrient supplies are suboptimal with respect to plant demand and demand increases due to enhanced plant production potential, tissue nutrient content increases [22].Recognition of growth-driven nutrient demand in turfgrass and what controls it has the potential for advancing understanding of many of the nuances of turfgrass responses to changes in external nutrient supplies. Variable nutrient demand at a fixed soil supply may account for difficulties encountered in soil test calibrations and interpretations for turfgrass [23], for reported differences in turfgrass species and cultivar nutrient requirements and nutrient use efficiencies [24–26], for lack of relationships between tissue cation and soil exchangeable cation concentrations [27, 28], and for lack of K luxury consumption by turfgrass [29].Despite these many potential manifestations and consequences, the significance of nutrient demand has not been thoroughly investigated for turfgrass. The primary objectives of this research were to assemble evidence that nutrient utilization by turfgrass has the characteristics of demand driven uptake, to ascertain the principal factors regulating turfgrass growth rates and nutrient demand, and to apply the concept in the interpretation of published results from turfgrass nutrition studies.


## 2. Materials and Methods

This report draws upon the results of field experiments conducted over a period of several years at the University of Wisconsin O.J. Noer Turfgrass Research and Education Facility located near Madison, WI, USA and soil and clippings gathered from golf courses throughout the state of WI. A brief description of each of four individual experiments follows.


### 2.1. Experiment  1: Soil Test Calibrations for Golf Putting Greens

Paired soil and clipping samples were collected from 419 putting greens on golf courses located throughout Wisconsin during the 2001 and 2002 growing seasons for the purpose of improving soil test calibrations. The golf course superintendents were given instructions for collecting the clippings on specific dates. On those dates, a researcher visited the golf course(s) to pick up the clippings and collect soil samples from the respective putting greens. Composite soil samples consisting of 20 randomly selected cores were taken to a 10 cm depth with a 1.6 cm diameter probe. The clipping and soil samples were transported that same day to the University of Wisconsin-Madison for processing and analysis.The soil samples were dried at 65°C, ground to pass through a 10-mesh sieve, and analyzed for Bray-1 P and K [30] by way of inductively coupled plasma-optical emission spectroscopy (ICP-OES). The grass clippings were at 65°C for 48 hours and then cleaned, first by hand removal of foreign matter and then by sieving and passing through a seed cleaner adjusted to remove contaminating soil. The cleaned clippings were ground in a stainless steel chambered Wiley mill outfitted with a 40-mesh sieve. Tissue N content was determined using the method of Bremner and Mulvaney [31]. Tissue samples digested with concentrated HNO3 and H2O2 [32] were analyzed for P, K, Ca, Mg, S, and micronutrients by ICP-OES at the Wisconsin State Soil and Plant Analysis Laboratory (SPAL) in Verona, WI, USA.Inspection of data from the 419 Wisconsin putting greens indicated that few if any of the greens had deficiency levels of nutrients. This led to the May 2003 reconstruction of a putting green for the purpose of creating what were deemed to be growth limiting levels of soil test P and K. Site preparation began with the removal of the existing sod to a 10 cm depth from a 10.9 × 16.4 m putting green constructed in 1992 according to USGA standards [33]. The upper 15 cm of root zone was removed to eliminate spatial differences that may have developed over the previous 11 years of use for research. The remaining 15 cm of root zone mix was mixed repeatedly with a tractor-mounted rotary tiller. The green was then capped with 15 cm of a commercial 85/15 (v/v) sand-peat root zone mix. After applying and raking in a 14-12.3-10 (N-P-K) starter fertilizer at the rate of 49 kg N ha−1, the area was seed to “SR 1119” creeping bentgrass (Agrostis stoloniferaL.). The green was placed under a grow-in program where irrigation four times daily gradually gave way to daily irrigation at 100% of estimated ET. Nitrogen fertilizer (urea; 46-0-0) was applied every 2 to 3 weeks to maintain satisfactory turfgrass color, and the putting green was sand top-dressed every 2 to 3 weeks to level the surface and allow for gradual reduction of the mowing height from the initial 1.3 cm to 0.3 cm by the end of the establishment year. In October 2003 the green was divided into three blocks, each consisting of three 3.6 by 5.5 m main plots for an N rate differential, three 1.2 by 5.5 m subplots for a K rate differential, and three 1.8 by 3.6 m sub-sub plots for a P rate differential. Urea (46-0-0), ammonium phosphate (11-21-0) and potassium sulfate (0-0-41.5) were applied to establish the nutrient differentials. Rates during the establishment year were 240, 265, and 338 kg N ha−1, 43, 116, and 146 kg P ha−1, and 35, 181, and 287 kg K ha−1.Nutrient rates in the year following putting green the 2003 establishment totaled 112, 254 and 356 kg N ha−1, 0, 43 and 86 kg P ha−1, and 0, 53 and 105 kg K ha−1. Mowing was 5 to 6 days per week at 0.3 cm and irrigation daily at 80% ET estimated from on-site weather data. Fungicides were correctively applied as needed to control dollar spot (Sclerotinia homoeocarpaF. Bennett). Clippings collected from 0.4 m2 plot areas in May, July, and October were dried at 65°C, weighed, cleaned, ground, and analyzed for total N, P, and K as described above. Soil samples were removed to a depth of 10 cm from all plots at the times of clipping collection and analyzed for Bray-1 extractable P and K at SPAL.


### 2.2. Experiment  2: Effects of Fertilization on Creeping Bentgrass Growth and Tissue Nutrient Content

This three-year field experiment consisted of four blocks of twelve 1.8 m × 2.4 m plots assigned to a 2-year old “Penncross” creeping bentgrass fairway established on Troxel silt loam (fine silty, mixed, superactive, and mesic Pachric Argiudoll). At the start of the study in 1992, the soil pH was 5.8, and Bray-1 levels of soil P and K were 62 mg kg−1 and 180 mg kg−1, respectively. The twelve treatments randomly assigned within each block consisted of a series of nutrient applications. The first series was annual N rates of 98, 195, or 390 kg ha−1 applied as a 25-2.2-8.3 (N-P-K) fertilizer with polymer + sulfur-coated urea as the primary N carrier. The second series of treatments consisted of N at an annual rate of 195 kg ha−1 applied with either 21 kg P ha−1, 121 kg K ha−1, or both. The P and K carriers were triple superphosphate (0-20-0) and potassium sulfate (0-0-41.5). The third series of treatments was 195 kg N + 21 kg P + 121 kg K ha−1 applied with different N carriers. The carriers were polymer + sulfur-coated urea, ammonium sulfate (21-0-0), and feed grade urea (46-0-0). The final three treatments involved fall and spring applications of elemental S at 195 kg ha−1 or ground dolomite limestone (neutralizing index of 90 to 95) at 2,440 kg ha−1 in conjunction with 195 kg N + 21 kg P + 121 kg K ha−1. Polymer + sulfur-coated urea served as the N carrier when the S was applied. Urea and ammonium sulfate were the N carriers for the lime treatments. All fertilizers were applied in four applications equally split between May, July, September, and October of each of the three years the study was conducted.The creeping bentgrass was maintained as a golf fairway with mowing at 1.3 cm every Monday, Wednesday, and Friday, and irrigation twice a week at 80% estimated ET. Fungicides were correctively applied as needed for disease control. Soil samples were annually collected from all plots to a 10 cm depth in 1.25 cm increments for measurement of Bray-1 soil test P and K at SPAL as described in Experiment  1. Grass clippings were collected monthly from 0.75 m2 plot areas, oven dried at 65°C, weighed, and ground for analysis using the same methods described in Experiment  1.


### 2.3. Experiment  3: Nitrogen Rates Required for Maximum Turfgrass Biomass Production

Two trials were conducted, the first on a 4-year old stand of Kentucky bluegrass (Poa pratensis L.) and the second on a 3-year old stand of “Penncross” creeping bentgrass (Agrostis stoloniferaL.) maintained as a golf course fairway. Soil on both sites was Troxel silt loam (fine silty, mixed, superactive, mesic Pachic Argiudoll) having a pH of 6.8 and Bray-1 soil tests of 60 to 62 mg P kg−1 and 120 to 140 mg K kg−1. Annual N rates for the Kentucky bluegrass were 0, 98, 195, 293, 390, 488, 585, and 780 kg ha−1 split into four equal applications made in May, July, August, and September to plots measuring 2.5 by 7.6 m. The N was applied as a 25-2.2-8.3 (N-P-K) grade fertilizer containing polymer + sulfur-coated urea as the N carrier. The site was irrigated twice weekly at 80% ET estimated from weather station data. Mowing was every 3 to 4 days at 6.4 cm and clippings removed. Clippings were collected from 0.8 m2 areas of each plot, dried at 65°C, and weighed. Nitrogen in the form of feed grade urea (46-0-0) was applied to 0.6 by 3.6 m plots on the creeping bentgrass fairway at rates of 0, 100, 214, 388, 684, 858, and 1,032 kg ha−1 split into 6 equally sized applications spaced evenly throughout the growing season. Irrigation was thrice weekly at 80% estimated ET. Mowing with clipping removal was at a height of 1.3 cm every other day. Clippings were collected at each mowing from 3.2 m2 plot areas, dried at 65°C, and weighed.


### 2.4. Experiment  4: Late-Season Creeping Bentgrass Responses to Trinexapac-Ethyl Applications

After judiciously applying P and K to the putting green employed in the soil test calibration study (Experiment  1) to adjust soil P and K to uniformly high levels, the green was divided into three blocks, each comprised of ten 2.4 by 3.6 m plots. In September 2005, treatments consisting of trinexapac-ethyl (TE) at rates of 0, 0.016, 0.032, and 0.064 mL/m2, each at intervals of 1, 2, and 3 weeks, were randomly assigned to the plots. Trinexapac-ethyl application was with a CO2-powered backpack sprayer calibrated to deliver 9.3 mL m−2. Clippings were collected weekly from 1.4 m2 plot areas, dried at 65°C, and weighed. The study was continued for a period of 7 weeks during September and October 2005. Select samples from the last two sets of clippings were bulked, ground, and analyzed for total nutrient content using the same methods as in Experiment 1.


### 2.5. Statistical Methods

Data for Experiments  1–4 were analyzed using regression analysis in the JMP statistical software package (Version 6.0; SAS Institute, Cary, NC). Data from Experiment  2 were also analyzed using analysis of variance followed by Duncan’s Least Statistical Difference (LSD) to separate treatment means at thealpha=0.05 level with the CoStat statistical software package (Version 6.4; CoHort Software, Monterey, CA, USA).


## 2.1. Experiment  1: Soil Test Calibrations for Golf Putting Greens

Paired soil and clipping samples were collected from 419 putting greens on golf courses located throughout Wisconsin during the 2001 and 2002 growing seasons for the purpose of improving soil test calibrations. The golf course superintendents were given instructions for collecting the clippings on specific dates. On those dates, a researcher visited the golf course(s) to pick up the clippings and collect soil samples from the respective putting greens. Composite soil samples consisting of 20 randomly selected cores were taken to a 10 cm depth with a 1.6 cm diameter probe. The clipping and soil samples were transported that same day to the University of Wisconsin-Madison for processing and analysis.The soil samples were dried at 65°C, ground to pass through a 10-mesh sieve, and analyzed for Bray-1 P and K [30] by way of inductively coupled plasma-optical emission spectroscopy (ICP-OES). The grass clippings were at 65°C for 48 hours and then cleaned, first by hand removal of foreign matter and then by sieving and passing through a seed cleaner adjusted to remove contaminating soil. The cleaned clippings were ground in a stainless steel chambered Wiley mill outfitted with a 40-mesh sieve. Tissue N content was determined using the method of Bremner and Mulvaney [31]. Tissue samples digested with concentrated HNO3 and H2O2 [32] were analyzed for P, K, Ca, Mg, S, and micronutrients by ICP-OES at the Wisconsin State Soil and Plant Analysis Laboratory (SPAL) in Verona, WI, USA.Inspection of data from the 419 Wisconsin putting greens indicated that few if any of the greens had deficiency levels of nutrients. This led to the May 2003 reconstruction of a putting green for the purpose of creating what were deemed to be growth limiting levels of soil test P and K. Site preparation began with the removal of the existing sod to a 10 cm depth from a 10.9 × 16.4 m putting green constructed in 1992 according to USGA standards [33]. The upper 15 cm of root zone was removed to eliminate spatial differences that may have developed over the previous 11 years of use for research. The remaining 15 cm of root zone mix was mixed repeatedly with a tractor-mounted rotary tiller. The green was then capped with 15 cm of a commercial 85/15 (v/v) sand-peat root zone mix. After applying and raking in a 14-12.3-10 (N-P-K) starter fertilizer at the rate of 49 kg N ha−1, the area was seed to “SR 1119” creeping bentgrass (Agrostis stoloniferaL.). The green was placed under a grow-in program where irrigation four times daily gradually gave way to daily irrigation at 100% of estimated ET. Nitrogen fertilizer (urea; 46-0-0) was applied every 2 to 3 weeks to maintain satisfactory turfgrass color, and the putting green was sand top-dressed every 2 to 3 weeks to level the surface and allow for gradual reduction of the mowing height from the initial 1.3 cm to 0.3 cm by the end of the establishment year. In October 2003 the green was divided into three blocks, each consisting of three 3.6 by 5.5 m main plots for an N rate differential, three 1.2 by 5.5 m subplots for a K rate differential, and three 1.8 by 3.6 m sub-sub plots for a P rate differential. Urea (46-0-0), ammonium phosphate (11-21-0) and potassium sulfate (0-0-41.5) were applied to establish the nutrient differentials. Rates during the establishment year were 240, 265, and 338 kg N ha−1, 43, 116, and 146 kg P ha−1, and 35, 181, and 287 kg K ha−1.Nutrient rates in the year following putting green the 2003 establishment totaled 112, 254 and 356 kg N ha−1, 0, 43 and 86 kg P ha−1, and 0, 53 and 105 kg K ha−1. Mowing was 5 to 6 days per week at 0.3 cm and irrigation daily at 80% ET estimated from on-site weather data. Fungicides were correctively applied as needed to control dollar spot (Sclerotinia homoeocarpaF. Bennett). Clippings collected from 0.4 m2 plot areas in May, July, and October were dried at 65°C, weighed, cleaned, ground, and analyzed for total N, P, and K as described above. Soil samples were removed to a depth of 10 cm from all plots at the times of clipping collection and analyzed for Bray-1 extractable P and K at SPAL.


## 2.2. Experiment  2: Effects of Fertilization on Creeping Bentgrass Growth and Tissue Nutrient Content

This three-year field experiment consisted of four blocks of twelve 1.8 m × 2.4 m plots assigned to a 2-year old “Penncross” creeping bentgrass fairway established on Troxel silt loam (fine silty, mixed, superactive, and mesic Pachric Argiudoll). At the start of the study in 1992, the soil pH was 5.8, and Bray-1 levels of soil P and K were 62 mg kg−1 and 180 mg kg−1, respectively. The twelve treatments randomly assigned within each block consisted of a series of nutrient applications. The first series was annual N rates of 98, 195, or 390 kg ha−1 applied as a 25-2.2-8.3 (N-P-K) fertilizer with polymer + sulfur-coated urea as the primary N carrier. The second series of treatments consisted of N at an annual rate of 195 kg ha−1 applied with either 21 kg P ha−1, 121 kg K ha−1, or both. The P and K carriers were triple superphosphate (0-20-0) and potassium sulfate (0-0-41.5). The third series of treatments was 195 kg N + 21 kg P + 121 kg K ha−1 applied with different N carriers. The carriers were polymer + sulfur-coated urea, ammonium sulfate (21-0-0), and feed grade urea (46-0-0). The final three treatments involved fall and spring applications of elemental S at 195 kg ha−1 or ground dolomite limestone (neutralizing index of 90 to 95) at 2,440 kg ha−1 in conjunction with 195 kg N + 21 kg P + 121 kg K ha−1. Polymer + sulfur-coated urea served as the N carrier when the S was applied. Urea and ammonium sulfate were the N carriers for the lime treatments. All fertilizers were applied in four applications equally split between May, July, September, and October of each of the three years the study was conducted.The creeping bentgrass was maintained as a golf fairway with mowing at 1.3 cm every Monday, Wednesday, and Friday, and irrigation twice a week at 80% estimated ET. Fungicides were correctively applied as needed for disease control. Soil samples were annually collected from all plots to a 10 cm depth in 1.25 cm increments for measurement of Bray-1 soil test P and K at SPAL as described in Experiment  1. Grass clippings were collected monthly from 0.75 m2 plot areas, oven dried at 65°C, weighed, and ground for analysis using the same methods described in Experiment  1.


## 2.3. Experiment  3: Nitrogen Rates Required for Maximum Turfgrass Biomass Production

Two trials were conducted, the first on a 4-year old stand of Kentucky bluegrass (Poa pratensis L.) and the second on a 3-year old stand of “Penncross” creeping bentgrass (Agrostis stoloniferaL.) maintained as a golf course fairway. Soil on both sites was Troxel silt loam (fine silty, mixed, superactive, mesic Pachic Argiudoll) having a pH of 6.8 and Bray-1 soil tests of 60 to 62 mg P kg−1 and 120 to 140 mg K kg−1. Annual N rates for the Kentucky bluegrass were 0, 98, 195, 293, 390, 488, 585, and 780 kg ha−1 split into four equal applications made in May, July, August, and September to plots measuring 2.5 by 7.6 m. The N was applied as a 25-2.2-8.3 (N-P-K) grade fertilizer containing polymer + sulfur-coated urea as the N carrier. The site was irrigated twice weekly at 80% ET estimated from weather station data. Mowing was every 3 to 4 days at 6.4 cm and clippings removed. Clippings were collected from 0.8 m2 areas of each plot, dried at 65°C, and weighed. Nitrogen in the form of feed grade urea (46-0-0) was applied to 0.6 by 3.6 m plots on the creeping bentgrass fairway at rates of 0, 100, 214, 388, 684, 858, and 1,032 kg ha−1 split into 6 equally sized applications spaced evenly throughout the growing season. Irrigation was thrice weekly at 80% estimated ET. Mowing with clipping removal was at a height of 1.3 cm every other day. Clippings were collected at each mowing from 3.2 m2 plot areas, dried at 65°C, and weighed.


## 2.4. Experiment  4: Late-Season Creeping Bentgrass Responses to Trinexapac-Ethyl Applications

After judiciously applying P and K to the putting green employed in the soil test calibration study (Experiment  1) to adjust soil P and K to uniformly high levels, the green was divided into three blocks, each comprised of ten 2.4 by 3.6 m plots. In September 2005, treatments consisting of trinexapac-ethyl (TE) at rates of 0, 0.016, 0.032, and 0.064 mL/m2, each at intervals of 1, 2, and 3 weeks, were randomly assigned to the plots. Trinexapac-ethyl application was with a CO2-powered backpack sprayer calibrated to deliver 9.3 mL m−2. Clippings were collected weekly from 1.4 m2 plot areas, dried at 65°C, and weighed. The study was continued for a period of 7 weeks during September and October 2005. Select samples from the last two sets of clippings were bulked, ground, and analyzed for total nutrient content using the same methods as in Experiment 1.


## 2.5. Statistical Methods

Data for Experiments  1–4 were analyzed using regression analysis in the JMP statistical software package (Version 6.0; SAS Institute, Cary, NC). Data from Experiment  2 were also analyzed using analysis of variance followed by Duncan’s Least Statistical Difference (LSD) to separate treatment means at thealpha=0.05 level with the CoStat statistical software package (Version 6.4; CoHort Software, Monterey, CA, USA).


## 3. Results and Discussion

### 3.1. Evidence for Nutrient Demand

If plant growth rate regulates nutrient demand and is the principal driving force for nutrient uptake [1–4], then nutrient uptake should be strongly dependent on growth rate. This was evident in data from Experiment  1, where regressions of nutrient uptake on creeping bentgrass growth rates yielded R2  values ranging from 0.910 to 0.982 for N, P, and K (Figure 1) and 0.884 to 0.932 for Ca, Mg and S (Figure 2).Figure 1
Uptake of N, P, and K uptake as affected by clipping yield for a creeping bentgrass (A. stolonifera) putting green (Experiment  1). All slopes were statistically significant at P<0.001 as indicated by ***.Figure 2
Daily uptake of  Ca, Mg, and S as affected by clipping yield for a creeping bentgrass (Agrostis stolonifera L.) putting green grown on a sand-matrix root zone (Experiment  1). All regression models were statistically significant at P<0.001 as indicated by ***.Another characteristic of plant nutrient demand is that once the external nutrient supply attains the level where demand is satisfied, tissue nutrient concentrations plateau, exhibiting little or no change with further increases in nutrient supply [21]. This pattern of turfgrass response to increasing nutrient supplies has been observed by other researchers and occurs regardless of whether the turf property measured is turfgrass quality [34], shoot counts, thatch thickness, relative yield, quality, tissue nutrient content, or root weight [23, 35].Clipping nutrient content plateaued in data collected from the 419 Wisconsin putting greens (Experiment  1). As shown in Figure3, there was no significant increase (P=0.62) in the mean tissue P content as Bray-1 P increased from 1.8 to 200 mg kg−1. This suggests that at the rates of N being applied plant demand was being met at the lowest P levels found in the study. For K (Figure 3), there was a slight increase in plant K across all levels of increasing soil K. This may indicate that, in addition to growth-induced plant demand, K uptake is also influenced to some degree by its prominent role in osmotic regulation [20].Figure 3
Relationship between Bray1-extractable soil P or K levels and tissue P or K content of cool season turfgrass species collected from 419 golf greens in Wisconsin (Experiment  1).Lack of turfgrass response to increased nutrient supplies when demand is already being satisfied was also evidenced in Experiment  2 conducted on a soil whose soil test P and K levels were approximately three times those considered to be optimum by University of Wisconsin-Extension recommendations [36]. Under these circumstances application of fertilizer P and K did not significantly alter clipping P and K content (Table 1). However, application of N alone to stimulate growth increased clipping N, P, and K content and rates of decline in soil test P and K paralleled to the N application rate (Table 2). This observation has the ironic implication that when soil supply of K is high and a turf manager seeks to increase tissue K content to enhance drought resistance, increase heat and traffic tolerance, or reduce winter injury [37], the most effective approach may be to apply N.Table 1
Influences of N, P, and K applications on creeping bentgrass clipping N, P, and K content for a site high in soil P and K (Experiment  2).
Nutrients appliedTurfgrass Clipping Nutrient ContentN-P-KNPKKg ha−1g kg−1195-0-042.64.425.4195-21-043.34.426.2195-0-12142.34.225.6195-21-12143.34.326.4Duncan’s LSD0.05NSNSNSTable 2
Influence of annual N rate on creeping bentgrass clipping N, P, and K content and reductions in soil test P and K for a site high in soil P and K (Experiment  2).
Annual N rateTurfgrass clipping nutrient contentReductions in Bray-1 soil test level over three yearsNPKPKkg ha−1g kg−1mg kg−19837.94.224.062519542.64.426.4103739052.34.829.41757Duncan’s LSD0.051.40.30.8311These experimental results provide three lines of evidence that turfgrass absorbs nutrients according to demand that is governed by growth rate. Growth rate typically accounts for more than 90% of the variation in nutrient uptake, once nutrient demand is satisfied, further increases in external supply have little influence on tissue content, and tissue nutrient content can vary widely at a given external supply due to differences in growth driven demand. The issue then becomes that of determining what growth factor or factors most commonly govern turfgrass growth.


### 3.2. Regulation of Turfgrass Nutrient Demand

In 2003, Bowman surmised that today’s fertility programs are purposely designed to moderate effects on turfgrass growth, the results being suboptimal growth rates and N deficiency as a normal condition. If true, then N applied at conventional rates should always induce rapid growth responses that remain well within the linear range of biomass production. Some evidence for this comes from the work of Goatly et al. [38]. Three rates of late season N applied to bermudagrass linearly increased clipping production and leaf N, P, and K content. Regression of their clipping N, P, and K content on N application rate yields R2 values of 0.860 to 0.961, indicating operation of growth-driven nutrient demand.Data from our Experiment  3 confirmed that, at conventional N rates, turfgrass growth is far from optimal. The rate of N required for maximum Kentucky bluegrass annual clipping production was in excess of 700 kg ha−1 and in excess of 1000 kg ha−1N yr−1 for a creeping bentgrass fairway (Figure 4). Rates of N recommended for Kentucky bluegrass lawns in the upper Midwest range from 150 to 250 kg ha−1yr−1. Annual N rates for bentgrass fairways range from 150 to 300 kg ha−1yr−1. According to Figure 4, these N rates are but 15–30% of the quantities required for maximum clipping production. This supports the contention of Bowman [39] that under normal fertilization practices turfgrass is continuously N deficient from the perspective of clipping production, setting up N supply as a prime factor controlling turfgrass growth-driven nutrient demand.Figure 4
Clipping production of a creeping bentgrass (Agrostis stolonifera) fairway and a Kentucky bluegrass (Poa pratensis) lawn as affected by annual N fertilization amount (Experiment  1). Both regression models were statistically significant at P<0.001 as indicated by ***.Another widespread cultural practice anticipated to have a controlling influence on turfgrass nutrient demand is application of plant growth regulators. In our Experiment  4, late season application of trinexapac-ethyl (TE) at three rates and three intervals resulted in 3 to 64% reductions in creeping bentgrass clipping production at a single N rate. Under these circumstances, clipping yields accounted for 94 to 99% of the variation in uptake of not only N, P, and K (Figure5), but Ca, Mg, and S as well (not shown).Figure 5
Daily uptake of N, P, and K as affected by clipping yield for a creeping bentgrass (Agrostis stolonifera L.) putting green grown on a sand-matrix root zone (Experiment  1). All regression models were statistically significant at P<0.001 as indicated by ***.Data presented by McCullough et al. [40] serve to further examine the effects of both N rate and TE on turfgrass growth and nutrient uptake relationships. They applied four rates of N with and without TE to a bermudagrass putting green over two years. The TE reduced clipping production by a nearly constant 67% over the four N rates but did not alter the rate of N required to maintain acceptable color at different periods of time. Nutrient removal by the clippings when TE was applied was decreased by 70%, almost the same as the average percent reduction in clipping production. According to their data, clipping production accounted for 83 to 99% of the variation in clipping removals of N, P, K, Ca, Mg, S, Cu, Fe, Mn, and Zn.The strong influences of N rate and TE on turfgrass growth do not preclude the possibility that environmental conditions may also have notable effects on turfgrass nutrient demand. In our Experiment  2, three N rates were imposed on a creeping bentgrass fairway over three years and clippings collected three times each year for weight determination and analysis. Across the three seasons N rate accounted for only 43% of the variation in N uptake (Figure6(a)). However, coefficients of determination (R2) for the individual months (time of year) ranged from 0.87 to 0.92 (Figure 6(b)). During May and July N uptake increased from 0.015 to 0.019 kg ha−1 da−1 per kg ha−1of N applied. In October, when declining air temperatures suppressed turfgrass growth, N uptake increased only 0.006 kg ha−1 for each kg ha−1 of N applied. But at all times N uptake increased linearly with N rate, as did uptakes of P and K (data not shown). This is the same circumstance that arises when a growth regulator is applied. The degree of turfgrass growth suppression is constant across N rates, maintaining linear increases in nutrient uptakes associated with N-induced growth and nutrient demand.Relationship between N application rate and N uptake for a creeping bentgrass putting green in July and October. Differing environmental conditions lead to different relationships between application rate and uptake as shown by linear regression with combined data (a) and separate regression lines (b) (Experiment  2). All regression models (both a and b) were statistically significant (P<0.001).
(a)(b)The data presented here provide convincing evidence that N supply is a primary factor governing turfgrass nutrient demand. Similarly, application of a plant growth regulator changes demand in accord with the degree of suppression of turfgrass growth at any given level of N application. While the rate of change in demand per unit of N applied is reduced, the strength of the relationship between nutrient uptake and N supply remains very high. The same circumstance appears to arise in the presence of growth-limiting environmental stresses such as suboptimal temperature.


### 3.3. Consequences of Turfgrass Nutrient Demand

There are two prominent consequences of nutrient demand regulation of nutrient uptake on turfgrass responses to increasing soil supplies of nutrients. One is wide variation in turfgrass response at specified soil test values of P and K. The other is a leveling-off of nutrient uptake and tissue nutrient content when nutrient supply exceeds demand. Research conducted by Johnson et al. [34], Guillard and Dest [35], and Woods et al. [23] and data from our work (Figure 3) clearly show wide ranges in tissue nutrient content at given soil test levels of nutrients. Irrespective of the turfgrass response parameter used to develop soil test calibrations, these studies encountered wide ranges in turfgrass response at any particular level of soil test P or K. The data presented by Johnson et al. [34] show that at any given level of soil test P turfgrass quality ratings varied by as much as 5 units on a scale of 1 to 9. Woods et al. [23] observed that creeping bentgrass tissue K content varied as much as 450 mmol kg−1 at a given level of soil test K for any and all methods used to estimate soil K.We surmised that the wide variation in turfgrass tissue contents of nutrients at given soil test is a reflection of variation in nutrient demand resulting from differences in N nutrition. Evidence for this was sought by sorting the data from Experiment  1 into different ranges in tissue N and calculating the mean tissue P or K content for each N range. Plots of these tissue P and K contents versus clipping N range revealed highly significant linear relationships withR2 values, respectively, of 0.934 and 0.986 for P and K (Figure 7). Recalling that the main source of the data set is paired clipping and soil samples collected from 419 Wisconsin putting greens, the implication is that such relationships hold over what may be assumed to be substantial differences in weather, cultural practices, and turfgrass species and cultivars.Figure 7
Phosphorus and K content as a function of tissue N content for 419 tissue samples collected from putting greens around the state. Each data point represents a mean of all points within a particular N range. For example the 4.25 % N data points for P and K are the averages for all tissue samples with an N content between 4.0% and 4.5% (n=75). Both regression models were statistically significant (P<0.001).The second consequence of demand-driven nutrient uptake across increasing soil supplies of nutrients is that once demand is satisfied at the growth rate sustained by the amount of N being applied, there is little or no additional turfgrass response when nutrient supplies exceed those required to satisfy demand [21]. This is evident in Figure 3 as well as in the data presented by other researchers [23, 34, 35]. The responses presumably plateau once physiological requirements for the nutrients are satisfied at the prevailing growth rates. This may well explain why there is no luxury uptake of K by turfgrass [29] and that uptakes of K, Ca, and Mg reflect their physiological requirements rather than their ratios on soil cation exchange sites [27].Turfgrass clipping nutrient content has been reported to change significantly over the course of a growing season even when nutrient supply is more than adequate. Davis [41] noted that Kentucky bluegrass clipping K content varied more with time of sampling than rate of K application. Waddington et al. [42] recorded seasonal variations of 2.5 to 5.6 g P kg−1 and 15 to 25 mg K kg−1 in creeping bentgrass. Comparable results have been reported by Hall and Miller [43] for Kentucky bluegrass. No attempts have been made to explain these seasonal changes in tissue P and K content and have been cited as a reason why tissue nutrient content is not an appropriate plant parameter for calibrating soil tests for turfgrass [37].Growth rate, the generator of nutrient demand, was investigated as the prime factor leading to time of season variations in turfgrass tissue nutrient P and K content. Analysis of data from Waddington et al. [42] revealed that their seasonally dependent creeping bentgrass clipping P content was strongly related to clipping N content (R2=0.956). The relationship of tissue K to N was not as strong (R2=0.540). However, their soil test K levels were well above what recent research indicates as being optimum for sand putting greens and were in the range where creeping bentgrass response plateaus [23]. In our Experiment  2 clippings were collected on five dates in a single season from a creeping bentgrass fairway established on a silt loam soil and subjected to several different fertilizer treatments. Time of season variations in tissue nutrient contents varied from 3.1 to 4.9 g kg−1 for P and 24 to 25.9 g kg−1 for K. These clipping P and K contents were found to be highly correlated with clipping N (R2=0.986 for P, 0.907 for K) and N uptake accounted for 98 to 99 percent of the seasonal variations in P and K uptakes. This is evidence that seasonal variations in turfgrass tissue nutrient content result from time-of-year variations in growth rate-induced nutrient demand.Considerable variability in nutrient use efficiency has been observed for different turfgrass species and their cultivars [24–27], raising the specter that choice of species or cultivar can significantly alter fertilizer requirements. The assumption has been that genetics somehow gives rise to turfgrass species and cultivar differences in nutrient use efficiencies. Sartain and Dudeck [27] found N use efficiencies of 2.38 g dry matter (DM) mg−1N taken up by bermudagrass, but only 0.133 g DM mg−1N for perennial ryegrass. When the growth rates of the two species are combined into a single data set, differences in growth rates explain 97.5 to 99.0% of the species differences in N, P, and K uptake. The data of Mehall et al. [24] for 15 field grown Kentucky bluegrass cultivars similarly show that differences in cultivar growth rates accounted for 73 to 84% of the differences in tissue P and K content. Menzel and Broomhall [26], who grew eight tropical turfgrass species under different fertility regimes, observed significant differences in growth responses and nutrient uptake. Analysis of their data shows that species differences in clipping production could account for 76 to 98% of the variations in N, P, and K uptakes.Liu et al. [25] reported significant differences in growth rates and K use efficiencies for six cultivars each of Kentucky bluegrass, perennial ryegrass, and tall fescue. They attributed differences in potassium use efficiencies of the various species and cultivars to genetically linked differences in K uptake kinetics. But inspection of their data reveals that, irrespective of species or cultivar, growth rates could account for over 94% of the observed variations in K uptake (Figure 8). This observation is consistent with reports that the nutrient uptake kinetic parameters Km   and  Cm, when measured for whole plants, are not genetic characteristics but vary due to changes in growth-related nutrient demand [44–46]. This, plus the data discussed above, serves as evidence that turfgrass species and cultivar differences in nutrient use efficiencies are largely manifestations of differences in genetic predispositions for biomass production in a given environment.Figure 8
Alternative analysis of data presented by Liu et al. [25] who concluded that differences in K uptake among 3 species of grasses and 6 cultivars of each grass were due to genetically linked differences in K uptake kinetics. However, reanalysis of the data (above) suggests that differences in growth rate (also genetically controlled) account for 94% of the variation in K uptake.


## 3.1. Evidence for Nutrient Demand

If plant growth rate regulates nutrient demand and is the principal driving force for nutrient uptake [1–4], then nutrient uptake should be strongly dependent on growth rate. This was evident in data from Experiment  1, where regressions of nutrient uptake on creeping bentgrass growth rates yielded R2  values ranging from 0.910 to 0.982 for N, P, and K (Figure 1) and 0.884 to 0.932 for Ca, Mg and S (Figure 2).Figure 1
Uptake of N, P, and K uptake as affected by clipping yield for a creeping bentgrass (A. stolonifera) putting green (Experiment  1). All slopes were statistically significant at P<0.001 as indicated by ***.Figure 2
Daily uptake of  Ca, Mg, and S as affected by clipping yield for a creeping bentgrass (Agrostis stolonifera L.) putting green grown on a sand-matrix root zone (Experiment  1). All regression models were statistically significant at P<0.001 as indicated by ***.Another characteristic of plant nutrient demand is that once the external nutrient supply attains the level where demand is satisfied, tissue nutrient concentrations plateau, exhibiting little or no change with further increases in nutrient supply [21]. This pattern of turfgrass response to increasing nutrient supplies has been observed by other researchers and occurs regardless of whether the turf property measured is turfgrass quality [34], shoot counts, thatch thickness, relative yield, quality, tissue nutrient content, or root weight [23, 35].Clipping nutrient content plateaued in data collected from the 419 Wisconsin putting greens (Experiment  1). As shown in Figure3, there was no significant increase (P=0.62) in the mean tissue P content as Bray-1 P increased from 1.8 to 200 mg kg−1. This suggests that at the rates of N being applied plant demand was being met at the lowest P levels found in the study. For K (Figure 3), there was a slight increase in plant K across all levels of increasing soil K. This may indicate that, in addition to growth-induced plant demand, K uptake is also influenced to some degree by its prominent role in osmotic regulation [20].Figure 3
Relationship between Bray1-extractable soil P or K levels and tissue P or K content of cool season turfgrass species collected from 419 golf greens in Wisconsin (Experiment  1).Lack of turfgrass response to increased nutrient supplies when demand is already being satisfied was also evidenced in Experiment  2 conducted on a soil whose soil test P and K levels were approximately three times those considered to be optimum by University of Wisconsin-Extension recommendations [36]. Under these circumstances application of fertilizer P and K did not significantly alter clipping P and K content (Table 1). However, application of N alone to stimulate growth increased clipping N, P, and K content and rates of decline in soil test P and K paralleled to the N application rate (Table 2). This observation has the ironic implication that when soil supply of K is high and a turf manager seeks to increase tissue K content to enhance drought resistance, increase heat and traffic tolerance, or reduce winter injury [37], the most effective approach may be to apply N.Table 1
Influences of N, P, and K applications on creeping bentgrass clipping N, P, and K content for a site high in soil P and K (Experiment  2).
Nutrients appliedTurfgrass Clipping Nutrient ContentN-P-KNPKKg ha−1g kg−1195-0-042.64.425.4195-21-043.34.426.2195-0-12142.34.225.6195-21-12143.34.326.4Duncan’s LSD0.05NSNSNSTable 2
Influence of annual N rate on creeping bentgrass clipping N, P, and K content and reductions in soil test P and K for a site high in soil P and K (Experiment  2).
Annual N rateTurfgrass clipping nutrient contentReductions in Bray-1 soil test level over three yearsNPKPKkg ha−1g kg−1mg kg−19837.94.224.062519542.64.426.4103739052.34.829.41757Duncan’s LSD0.051.40.30.8311These experimental results provide three lines of evidence that turfgrass absorbs nutrients according to demand that is governed by growth rate. Growth rate typically accounts for more than 90% of the variation in nutrient uptake, once nutrient demand is satisfied, further increases in external supply have little influence on tissue content, and tissue nutrient content can vary widely at a given external supply due to differences in growth driven demand. The issue then becomes that of determining what growth factor or factors most commonly govern turfgrass growth.


## 3.2. Regulation of Turfgrass Nutrient Demand

In 2003, Bowman surmised that today’s fertility programs are purposely designed to moderate effects on turfgrass growth, the results being suboptimal growth rates and N deficiency as a normal condition. If true, then N applied at conventional rates should always induce rapid growth responses that remain well within the linear range of biomass production. Some evidence for this comes from the work of Goatly et al. [38]. Three rates of late season N applied to bermudagrass linearly increased clipping production and leaf N, P, and K content. Regression of their clipping N, P, and K content on N application rate yields R2 values of 0.860 to 0.961, indicating operation of growth-driven nutrient demand.Data from our Experiment  3 confirmed that, at conventional N rates, turfgrass growth is far from optimal. The rate of N required for maximum Kentucky bluegrass annual clipping production was in excess of 700 kg ha−1 and in excess of 1000 kg ha−1N yr−1 for a creeping bentgrass fairway (Figure 4). Rates of N recommended for Kentucky bluegrass lawns in the upper Midwest range from 150 to 250 kg ha−1yr−1. Annual N rates for bentgrass fairways range from 150 to 300 kg ha−1yr−1. According to Figure 4, these N rates are but 15–30% of the quantities required for maximum clipping production. This supports the contention of Bowman [39] that under normal fertilization practices turfgrass is continuously N deficient from the perspective of clipping production, setting up N supply as a prime factor controlling turfgrass growth-driven nutrient demand.Figure 4
Clipping production of a creeping bentgrass (Agrostis stolonifera) fairway and a Kentucky bluegrass (Poa pratensis) lawn as affected by annual N fertilization amount (Experiment  1). Both regression models were statistically significant at P<0.001 as indicated by ***.Another widespread cultural practice anticipated to have a controlling influence on turfgrass nutrient demand is application of plant growth regulators. In our Experiment  4, late season application of trinexapac-ethyl (TE) at three rates and three intervals resulted in 3 to 64% reductions in creeping bentgrass clipping production at a single N rate. Under these circumstances, clipping yields accounted for 94 to 99% of the variation in uptake of not only N, P, and K (Figure5), but Ca, Mg, and S as well (not shown).Figure 5
Daily uptake of N, P, and K as affected by clipping yield for a creeping bentgrass (Agrostis stolonifera L.) putting green grown on a sand-matrix root zone (Experiment  1). All regression models were statistically significant at P<0.001 as indicated by ***.Data presented by McCullough et al. [40] serve to further examine the effects of both N rate and TE on turfgrass growth and nutrient uptake relationships. They applied four rates of N with and without TE to a bermudagrass putting green over two years. The TE reduced clipping production by a nearly constant 67% over the four N rates but did not alter the rate of N required to maintain acceptable color at different periods of time. Nutrient removal by the clippings when TE was applied was decreased by 70%, almost the same as the average percent reduction in clipping production. According to their data, clipping production accounted for 83 to 99% of the variation in clipping removals of N, P, K, Ca, Mg, S, Cu, Fe, Mn, and Zn.The strong influences of N rate and TE on turfgrass growth do not preclude the possibility that environmental conditions may also have notable effects on turfgrass nutrient demand. In our Experiment  2, three N rates were imposed on a creeping bentgrass fairway over three years and clippings collected three times each year for weight determination and analysis. Across the three seasons N rate accounted for only 43% of the variation in N uptake (Figure6(a)). However, coefficients of determination (R2) for the individual months (time of year) ranged from 0.87 to 0.92 (Figure 6(b)). During May and July N uptake increased from 0.015 to 0.019 kg ha−1 da−1 per kg ha−1of N applied. In October, when declining air temperatures suppressed turfgrass growth, N uptake increased only 0.006 kg ha−1 for each kg ha−1 of N applied. But at all times N uptake increased linearly with N rate, as did uptakes of P and K (data not shown). This is the same circumstance that arises when a growth regulator is applied. The degree of turfgrass growth suppression is constant across N rates, maintaining linear increases in nutrient uptakes associated with N-induced growth and nutrient demand.Relationship between N application rate and N uptake for a creeping bentgrass putting green in July and October. Differing environmental conditions lead to different relationships between application rate and uptake as shown by linear regression with combined data (a) and separate regression lines (b) (Experiment  2). All regression models (both a and b) were statistically significant (P<0.001).
(a)(b)The data presented here provide convincing evidence that N supply is a primary factor governing turfgrass nutrient demand. Similarly, application of a plant growth regulator changes demand in accord with the degree of suppression of turfgrass growth at any given level of N application. While the rate of change in demand per unit of N applied is reduced, the strength of the relationship between nutrient uptake and N supply remains very high. The same circumstance appears to arise in the presence of growth-limiting environmental stresses such as suboptimal temperature.


## 3.3. Consequences of Turfgrass Nutrient Demand

There are two prominent consequences of nutrient demand regulation of nutrient uptake on turfgrass responses to increasing soil supplies of nutrients. One is wide variation in turfgrass response at specified soil test values of P and K. The other is a leveling-off of nutrient uptake and tissue nutrient content when nutrient supply exceeds demand. Research conducted by Johnson et al. [34], Guillard and Dest [35], and Woods et al. [23] and data from our work (Figure 3) clearly show wide ranges in tissue nutrient content at given soil test levels of nutrients. Irrespective of the turfgrass response parameter used to develop soil test calibrations, these studies encountered wide ranges in turfgrass response at any particular level of soil test P or K. The data presented by Johnson et al. [34] show that at any given level of soil test P turfgrass quality ratings varied by as much as 5 units on a scale of 1 to 9. Woods et al. [23] observed that creeping bentgrass tissue K content varied as much as 450 mmol kg−1 at a given level of soil test K for any and all methods used to estimate soil K.We surmised that the wide variation in turfgrass tissue contents of nutrients at given soil test is a reflection of variation in nutrient demand resulting from differences in N nutrition. Evidence for this was sought by sorting the data from Experiment  1 into different ranges in tissue N and calculating the mean tissue P or K content for each N range. Plots of these tissue P and K contents versus clipping N range revealed highly significant linear relationships withR2 values, respectively, of 0.934 and 0.986 for P and K (Figure 7). Recalling that the main source of the data set is paired clipping and soil samples collected from 419 Wisconsin putting greens, the implication is that such relationships hold over what may be assumed to be substantial differences in weather, cultural practices, and turfgrass species and cultivars.Figure 7
Phosphorus and K content as a function of tissue N content for 419 tissue samples collected from putting greens around the state. Each data point represents a mean of all points within a particular N range. For example the 4.25 % N data points for P and K are the averages for all tissue samples with an N content between 4.0% and 4.5% (n=75). Both regression models were statistically significant (P<0.001).The second consequence of demand-driven nutrient uptake across increasing soil supplies of nutrients is that once demand is satisfied at the growth rate sustained by the amount of N being applied, there is little or no additional turfgrass response when nutrient supplies exceed those required to satisfy demand [21]. This is evident in Figure 3 as well as in the data presented by other researchers [23, 34, 35]. The responses presumably plateau once physiological requirements for the nutrients are satisfied at the prevailing growth rates. This may well explain why there is no luxury uptake of K by turfgrass [29] and that uptakes of K, Ca, and Mg reflect their physiological requirements rather than their ratios on soil cation exchange sites [27].Turfgrass clipping nutrient content has been reported to change significantly over the course of a growing season even when nutrient supply is more than adequate. Davis [41] noted that Kentucky bluegrass clipping K content varied more with time of sampling than rate of K application. Waddington et al. [42] recorded seasonal variations of 2.5 to 5.6 g P kg−1 and 15 to 25 mg K kg−1 in creeping bentgrass. Comparable results have been reported by Hall and Miller [43] for Kentucky bluegrass. No attempts have been made to explain these seasonal changes in tissue P and K content and have been cited as a reason why tissue nutrient content is not an appropriate plant parameter for calibrating soil tests for turfgrass [37].Growth rate, the generator of nutrient demand, was investigated as the prime factor leading to time of season variations in turfgrass tissue nutrient P and K content. Analysis of data from Waddington et al. [42] revealed that their seasonally dependent creeping bentgrass clipping P content was strongly related to clipping N content (R2=0.956). The relationship of tissue K to N was not as strong (R2=0.540). However, their soil test K levels were well above what recent research indicates as being optimum for sand putting greens and were in the range where creeping bentgrass response plateaus [23]. In our Experiment  2 clippings were collected on five dates in a single season from a creeping bentgrass fairway established on a silt loam soil and subjected to several different fertilizer treatments. Time of season variations in tissue nutrient contents varied from 3.1 to 4.9 g kg−1 for P and 24 to 25.9 g kg−1 for K. These clipping P and K contents were found to be highly correlated with clipping N (R2=0.986 for P, 0.907 for K) and N uptake accounted for 98 to 99 percent of the seasonal variations in P and K uptakes. This is evidence that seasonal variations in turfgrass tissue nutrient content result from time-of-year variations in growth rate-induced nutrient demand.Considerable variability in nutrient use efficiency has been observed for different turfgrass species and their cultivars [24–27], raising the specter that choice of species or cultivar can significantly alter fertilizer requirements. The assumption has been that genetics somehow gives rise to turfgrass species and cultivar differences in nutrient use efficiencies. Sartain and Dudeck [27] found N use efficiencies of 2.38 g dry matter (DM) mg−1N taken up by bermudagrass, but only 0.133 g DM mg−1N for perennial ryegrass. When the growth rates of the two species are combined into a single data set, differences in growth rates explain 97.5 to 99.0% of the species differences in N, P, and K uptake. The data of Mehall et al. [24] for 15 field grown Kentucky bluegrass cultivars similarly show that differences in cultivar growth rates accounted for 73 to 84% of the differences in tissue P and K content. Menzel and Broomhall [26], who grew eight tropical turfgrass species under different fertility regimes, observed significant differences in growth responses and nutrient uptake. Analysis of their data shows that species differences in clipping production could account for 76 to 98% of the variations in N, P, and K uptakes.Liu et al. [25] reported significant differences in growth rates and K use efficiencies for six cultivars each of Kentucky bluegrass, perennial ryegrass, and tall fescue. They attributed differences in potassium use efficiencies of the various species and cultivars to genetically linked differences in K uptake kinetics. But inspection of their data reveals that, irrespective of species or cultivar, growth rates could account for over 94% of the observed variations in K uptake (Figure 8). This observation is consistent with reports that the nutrient uptake kinetic parameters Km   and  Cm, when measured for whole plants, are not genetic characteristics but vary due to changes in growth-related nutrient demand [44–46]. This, plus the data discussed above, serves as evidence that turfgrass species and cultivar differences in nutrient use efficiencies are largely manifestations of differences in genetic predispositions for biomass production in a given environment.Figure 8
Alternative analysis of data presented by Liu et al. [25] who concluded that differences in K uptake among 3 species of grasses and 6 cultivars of each grass were due to genetically linked differences in K uptake kinetics. However, reanalysis of the data (above) suggests that differences in growth rate (also genetically controlled) account for 94% of the variation in K uptake.


## 4. Conclusions

Three prominent characteristics of plant growth-driven nutrient demand are: (1) nutrient uptake and tissue content are more closely related to growth rates than external nutrient supply; (2) nutrient uptake at a given level of external supply varies substantially in response to variable nutrient demand; (3) tissue nutrient content tends to remain constant once external nutrient supplies allow plants to satisfy their demand. Our research (Figures1, 2, and 3) confirmed that turfgrass exhibits all of these characteristics.Nitrogen application at conventional rates of 150–300 kg ha−1yr−1 on a creeping bentgrass fairway and 146 to 195 kg ha−1 season−1 on a Kentucky bluegrass lawn resulted in clipping yields that were 15 to 35% of the maximums. This distinguishes turfgrass from most field crops where N rates are geared toward optimum biomass production. In turfgrass the suboptimal N supply is a major determinant of turfgrass growth rate-driven nutrient demand. Evidence for this was the strong dependencies of uptakes of N, P, K, Ca, Mg, and S on turfgrass growth and tissue N uptake, both indicators of nutrient demand. Application of a PGR or environmental stresses associated with time of season modified turfgrass response to increasing N rates but did not alter the relationships of growth rate or tissue N to tissue content of other nutrients.The prominence of nitrogen-driven nutrient demand in turfgrass may account for the fact that turfgrass does not accumulate what might be considered luxury amounts of K and the lack of a relationship between plant K, Ca, and Mg content and the ratios of the cations on the soil exchange complex. These observations support the contention that tissue nitrogen content may need to be considered for establishment of critical soil test values for turfgrass.



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*Source: 359284-2012-03-01.xml*