Abstract
Reestablishment of damaged golf greens and fairways planted to creeping bentgrass (Agrostis stolonifera), colonial bentgrass (A. capillaris), and velvet bentgrass (A. canina) is a common practice following winter injuries. Identifying bentgrass species (Agrostis sp.) and cultivars with the potential to establish under low soil temperatures would be beneficial to achieving more mature stands earlier in the spring. Twelve bentgrass cultivars, including seven cultivars of creeping bentgrass (007, 13-M, Declaration, L-93, Memorial, Penncross, and T-1), two colonial bentgrass cultivars (Capri and Tiger II), and three velvet bentgrass cultivars (Greenwich, SR-7200, and Villa), along with ‘Barbeta’ perennial ryegrass (Lolium perenne) were evaluated for grass cover in the field during early spring. Bentgrass species and cultivars were seeded in the field at the same seed count per unit area. Soil temperatures were monitored in unseeded check plots from initial planting date on 8 Apr. to termination on 29 May 2013. Soil temperatures increased linearly during the 52-day experimental period from 4.7 to 23.5 °C. All species and cultivars emerged at ≈10 °C soil temperature. Bentgrass species and cultivars varied only 2 to 3 days in their initial seedling emergence, while days varied among bentgrasses from 5.5 days (to 10% cover) to 8.6 days (to 90% cover). All velvet bentgrass cultivars required higher soil temperatures (13.6 °C) and more time (26 days) following initial seedling emergence to establish to 90% cover in the early spring. Creeping bentgrass cultivars 007, 13-M, and Memorial, along with colonial bentgrass cultivars Capri and Tiger II, were statistically equal to ‘Barbeta’ perennial ryegrass in their capacity after seedling emergence to achieve faster cover at lower soil temperatures. Heavier (larger) bentgrass seed was associated with faster cover during the early stages of establishment, but seed size was uncorrelated with establishment during later stages from 50% to 90% cover.
Golf greens and fairways planted to creeping bentgrass (Agrostis stolonifera), colonial bentgrass (A. capillaris), and velvet bentgrass (A. canina) require overseeding to reestablishment areas damaged from winter injuries. Cold soil temperatures (≈10 °C) typical of early spring plantings in the northern United States reduce seed germination and establishment vigor of cool-season grasses when compared with more favorable soil temperatures of 20 to 30 °C (He et al., 2013; Liu et al., 2001; McGinnies, 1960; Wright et al., 1978). Delayed growth shortens the growing period of seedling grasses and results in lower plant numbers in turf stands (Larsen et al., 2004), which are more susceptible to competition for moisture and summer drought (Young and Evans, 1982) and to competition from weeds during the establishment phase (Murphy et al., 2005).
Seed germination is the initial step in establishment, and rapid establishment can mitigate costs and revenue loss when golf courses openings are delayed. High-quality seed and seedling vigor is characterized by high viability (more germinating seeds). Emergence is the point that the primary leaf emerges from the soil surface followed by growth and development of roots, stolons, and rhizomes to form a dense turf. Seedling emergence, seedling vigor, and mature plant growth are distinct but related stages. Numerous studies have investigated laboratory seed germination characteristics such as final germination percentage and mean germination times that are conducted under controlled temperatures and moisture. It has been suggested the rate of growth after emergence is determined largely by the genotype and environment and not by the rate of seed germination (Argerich et al., 1990; Scott and Jones, 1985; Yamamoto et al., 1997a). For example, Yamamoto et al. (1997b) found the rate of emergence of the second and third leaves in kentucky bluegrass (Poa pratensis) to be under genetic control.
Unlike controlled environments, seeds are exposed to variable and unfavorable temperature and soil moisture in the field that delay and postpone germination, thereby affecting establishment (Happ et al., 1993). Germination of rough bluegrass (Poa trivialis) in the growth chamber at 10 °C provided two to three times the germination rate observed in the field when rough bluegrass was over-seeded into hybrid bermudagrass (Cynodon dactylon × C. transvaalensis) putting greens (Liu et al., 2001). Emergence of perennial ryegrass (Lolium perenne) seeded on compacted soil cores was only 40% to 69% of that observed under optimal germination when assayed on moist paper (Snapp et al., 2008). Total emergence and emergence rates in the field have been shown to be lower than emergence responses in the laboratory for cool-season range grasses (Hardegree and Van Vactor, 2000). These same authors reported greater germination in laboratory tests than measured in the field during early spring planting dates. Laycock and Shildrick (1979), however, found some positive correlation between perennial ryegrass laboratory germination and initial establishment measured in the field during the time between the sowing date (seed germination and emergence phase) and before the first mowing (maturity).
Soil temperature, water potential, and oxygen levels are important environmental factors affecting seed germination and influencing the seedlings to emerge from the soil (Burris, 1976; Pollock, 1972; Powell, 1988). Beard (1979) found the base temperatures (Tb), below which no germination is observed, to be ≈7 °C for perennial ryegrass and 11 °C for creeping bentgrass. Trudgill et al. (2000) reported colonial bentgrass Tb of 8 °C, and perennial ryegrass exhibited a Tb of 5 °C. The final stage of establishment involves mature roots, shoots, and lateral stems to form, which is a distinctly different phase from seed germination and emergence (Beard, 1973). As such, constant temperature and moisture regimes typical of germination laboratory tests are not necessarily predictive of field performance (Steiner et al., 1989; Trawatha et al., 1990).
Seed requires an accumulation of time and temperature (“thermal-time”) above Tb to germinate (Larsen and Bibby, 2005; Larsen et al., 2004) and in turn, to establish. Nonlinear regression thermal-time models have been used for seed germination and emergence (Larsen and Bibby, 2005; Larsen et al., 2004; Zhang et al., 2013). Monitoring soil temperatures after seedling emergence in the field until a mature stand is formed (i.e., requiring frequent mowing) has not been investigated in bentgrass species (Agrostis sp.) and cultivars. Growing degree day (GDD) models have been computed using soil or air temperatures collected daily. Base temperature varies with the crop with GDD for warm-season turfgrass establishment calculated using Tb close to 5 °C (Frank et al., 1998; Patton et al., 2004; Shahba and Qian, 2008; Unruh et al., 1996), while for cool-season lawn grass species, values of Tb for seed germination ranged from 1.6 to 3.6 °C (Larsen and Bibby, 2005), with bentgrass species exhibiting Tb closer to 10 °C (Heineck et al., 2018; Trudgill et al., 2000).
Identifying bentgrass species and cultivars with the potential to establish under low soil temperatures would be beneficial toward achieving more mature stands earlier in the spring. Simulated field-temperature studies have been conducted in cool-season range grasses (Hardegree and Van Vactor, 1999), cool-season lawn grasses (Larsen and Bibby, 2005), and in cool-season turfgrass for golf use such as bentgrass species and cultivars (Heineck et al., 2018). However, these responses were not validated in the field. Subsequently, Hardegree and Van Vactor (2000) reevaluated their previous findings and found simulated soil temperature models predicted greater germination than measured in the field, and they reported total emergence in the field to be more variable. While bentgrass species and cultivars have been tested in laboratory settings, there is a need to study cold temperature germination of these grasses in the field. Our research objective was to identify bentgrass species and cultivars with the capacity to establish to maturity in the shortest time and under cooler soil temperatures during an early spring planting date.
Materials and methods
The study was conducted on a Hadley silt loam (coarse-silty, mixed, superactive, nonacid, mesic Typic Udifluvents) located at the Joseph Troll Turf Research and Education Center at the University of Massachusetts Amherst in South Deerfield, MA. The Hadley silt-loam soil is characterized as 23.5% sand, 63.8% silt, and 12.7% clay. A field study was prepared and planted on 8 Apr. 2013 to assess germination vigor and percent grass cover during establishment. Twelve bentgrasses, including seven cultivars of creeping bentgrass (007, 13-M, Declaration, L-93, Memorial, Penncross, T-1), two cultivars of colonial bentgrass (Capri, Tiger II), and three cultivars of velvet bentgrass (Greenwich, SR-7200, Villa), were selected. All seed was fresh seed (harvested from 2012) and planted within 1 year of the test date.
Seeding rates were adjusted using seed count and germination rate (Table 1) to deliver the same approximate live seed per unit area to 3- × 3-ft plots, which also corresponded to the typical seeding rate for bentgrass species. Seed weight was determined for each of the 12 bentgrass species and cultivars by counting and weighing three replicates of 100 seeds. Seed germination was determined on seed following surface sterilization using 95% ethanol and 2% sodium hypochlorite solution, and then storing these at 5 °C before germination tests. Sterilized seed was placed in petri dishes containing moistened filter paper. The germination test was conducted with two replicates using petri dishes seeded with 50 seeds of a single cultivar, used as experiential units. Petri dishes were placed in a growth chamber under an 8-h photoperiod and low light levels (photosynthetic photon flux density of ≈60 µmol·m−2·s−1). Distilled water was applied as necessary to prevent filter paper and seed from drying out, and dishes were rotated to minimize any chamber effects. Germination temperature was set to 25 °C, with final germination recorded daily for up to 21 d, or until maximum germination percentage was reached and no additional germination was observed. Seed germination was based on the emergence of a visible shoot.
Seed characteristics for bentgrass species and cultivars.


Plots were seeded to bare-soil by hand immediately after ground thaw and when the ground could be properly prepared for planting. Before seeding, plots were tilled and weeds were removed. Plots were planted as a randomized complete block design using three replicates. ‘Barbeta’ perennial ryegrass was also included as part of the field test as a reference species because of its rapid germination and establishment rate. Bentgrass plots were not mowed during the establishment period until a total plant height of 1/2 inch was achieved. Thereafter, all bentgrass plots were mowed three times per week at a 3/8-inch height of cut with lightweight (walk-behind) reel mowers, with clippings collected. Perennial ryegrass check plots were mowed weekly at a 2-inch height of cut using rotary mowers, with clippings collected.
Initial seedling (coleoptile) emergence was recorded daily. Grass cover during establishment was recorded on a 2- to 6-d interval until 29 May 2013. Grass cover was measured using an intersect grid. The length and width of the grid measured the same as the length and width of the main plots (3 × 3 ft) and formed 100 (10 × 10) intersects. Therefore, counts were based on a total number of 100 intersects calculated as percent green cover. Cover was indirectly measured using canopy reflectance indices with a multispectral radiometer (CropScan, Rochester, MN). These indices provide indirect measures of turfgrass canopy properties such as color and biomass, and they have shown good correlations with response to various agronomic practices and stresses (Jiang, 2008; Johnsen et al., 2009; Lee et al., 2011). Measurements were taken about around the same time (1 to 3 d) of visual grass cover, using the intersect grid, but only on clear, sunny days between 1100 and 1300 HR. Normalized difference vegetation index (NDVI) was used to estimate aboveground green biomass and was calculated using the reflectance (R) of wavelengths in the red and near IR regions, including 660 and 940 nm, and calculated as follows: (R940 − R660)/(R940 + R660).
No protective covers were used at the time of planting so that initial emergence as well as visual estimates of weekly grass cover could be effectively assessed. Irrigation was applied as needed to maintain adequate soil moisture for germination. Soil pH according to soil test results was 5.5 before planting, with soil phosphorus (P) and potassium (K) to be medium-high and high, respectively. After all plots had shown initial emergence, 18N–10.5P–4.2K fertilizer was applied at 0.5 lb/1000 ft2 P as recommended by soil test results. Siduron (Tupersan; PBI Gordan, Shawnee, KS) was applied on 14 May 2013 at 4 lb/acre a.i. for preventative control of annual grassy weeds.
Temperature probes were installed in two adjacent, nonseeded check plots to record soil surface temperatures at a 1/2-inch soil depth. Soil temperatures were recorded throughout the experimental period, from the time when plots were initially planted until termination of the study on 29 May 2013. Soil temperature was recorded every 10 min but was averaged daily. In addition, GDD were computed using soil temperatures collected daily and averaged over a 24-h period. The general equation for GDD was [(maximum + minimum)/2] − Tb.
where y = percent cover; y0 = lower asymptote of y on the curve; x0 = the midpoint value for x (inflection point) between the upper and lower asymptote of the curve; a = upper asymptote for y on the curve; b = slope at the inflection point for x0 or the difference in x-values between 75% and 25% of the amplitude. Two data sets (i.e., x-variables) were fitted using the sigmoidal model described previously, with 1) the value for x as time (days) after emergence was used to compute y, and 2) the value x using the soil temperature average monitored in the check was used to compute y in the above equation. In both cases, the same percent cover was used. At initial seedling emergence (Table 2), time (days) as the independent variable x was “0,” and cover as the response variable y was assumed to be about “0”. Thereafter, response-y and independent-x variables were equal to measured cover at its corresponding time (days) of measurement. Similarly, initial soil temperature average at emergence was x as reported in Table 2, and the response variable y as cover was “0,” with response-y and independent-x variables thereafter equal to measured cover at its corresponding soil temperature average recorded in check plots. Measurements for y as cover and x as time (days) after emergence or soil temperature averages were recorded until 29 May 2013. In total, 11 d or soil temperature averages and their corresponding cover for each plot (experimental unit) were used to fit the data according to the above sigmoidal model and to compute the associated parameters y0, x0, a, and b. Following curve fitting, time (days) or soil temperatures to achieve 10%, 50%, and 90% cover was determined by back calculation using fitted sigmoidal parameters.
Days and soil temperature (°C) to achieve 10%, 50% and 90% grass cover among bentgrass species and cultivars following planting on 8 Apr. 2013. Grass cover during establishment was recorded on a 2- to 6-d interval until 29 May 2013.


Calculated days or soil temperatures between 10% to 90% cover follow a linear trend on the sigmoidal curve, and therefore linear regression slopes were calculated for each experimental plot to determine grass cover per unit day or grass cover per unit °C using simple linear regression. Slope estimates serve as indicators for the rate of grass establishment. Higher slope estimates per unit day indicated faster grass cover per day from 10% to 90% cover, while higher slope estimates per unit °C indicated greater capacity for cover during establishment from 10% to 90% cover under the cooler soil conditions in early spring.
Data including slope estimates, time (days), and soil temperature to achieve 10%, 50%, and 90% cover; cumulative soil temperature to achieve 10%, 50%, and 90% cover; along with actual cover and NDVI data by week were analyzed using Minitab statistical software (version 14; Minitab, State College, PA). The 12 bentgrass species and cultivars as treatments were analyzed as a randomized complete block design, with species and their cultivars as main plots using analysis of variance (ANOVA). One-way ANOVA was used to separate species (i.e., creeping bentgrass, colonial bentgrass, and velvet bentgrass) differences using 95% confidence intervals. Least significant difference values at α = 0.05 level were computed to separate between treatments among main effects due to bentgrass species and cultivars. No serious departures from the assumptions of ANOVA were detected in homogeneity of variance or normality. Correlation coefficients (r) were computed to assess the relationship among various response variables. Turf performance index (TPI) was used to categorize bentgrass species and cultivars according to their rank performance based on cover and NDVI. This nonparametric test is used to combine an overall assessment of groundcover as the number of times a bentgrass species and cultivar performed in the highest statistical grouping.
Results and discussion
Soil temperatures at the 1/2-inch soil depth increased linearly at a rate of 0.21 °C·d−1 during the experimental period from 8 Apr. (planting date) until termination on 31 May 2013 (Fig. 1). Hardegree and Van Vactor (2000) reported a similar warming rate of 0.18 °C·d−1 at a soil depth of 0.4 inch in Idaho from winter to early spring. Daily temperature averages during our study ranged from 4.7 °C on 11 Apr. to 23.5 °C on 30 May (Fig. 1). These soil temperature ranges represent suboptimal and optimal temperatures for cool-season turfgrass seed germination (McGinnies, 1960). The lowest recorded soil temperature (4.7 °C) was ≈4 to 5 °C below Tb for germination of bentgrass species (Beard, 1979; Trudgill et al., 2000) but close to Tb for perennial ryegrass (Beard, 1979; Larsen and Bibby, 2005; Trudgill et al., 2000). Initial soil temperature for seedling emergence for perennial ryegrass was 9.8 °C in all plots at day 9 after planting. Most creeping bentgrass cultivars emerged 1 d after perennial ryegrass at day 10 after planting (Table 2). Velvet bentgrass cultivars emerged last on day 13 after planting at 10.4 °C. Average daily soil temperatures were variable day-to-day during this early spring period, with the linear trend (r2) accounting for 55.3% of the total variation (Fig. 1). Soil temperature varies widely day-to-day with weather conditions, which is typical for this spring period (Hardegree and Van Vactor, 2000; Larsen and Bibby, 2005).

Daily soil temperature average recorded during the experimental period. Soil sensors were imbedded near the soil surface [1/2-inch (1.27-cm) soil depth] in unseeded check plots. Soil temperatures ranged from 4.7 to 23.5 °C during 52 d following planting on 8 Apr. 2013; (1.8 × °C) + 32 = °F.
Citation: HortTechnology hortte 31, 1; 10.21273/HORTTECH04653-20

Daily soil temperature average recorded during the experimental period. Soil sensors were imbedded near the soil surface [1/2-inch (1.27-cm) soil depth] in unseeded check plots. Soil temperatures ranged from 4.7 to 23.5 °C during 52 d following planting on 8 Apr. 2013; (1.8 × °C) + 32 = °F.
Citation: HortTechnology hortte 31, 1; 10.21273/HORTTECH04653-20
Daily soil temperature average recorded during the experimental period. Soil sensors were imbedded near the soil surface [1/2-inch (1.27-cm) soil depth] in unseeded check plots. Soil temperatures ranged from 4.7 to 23.5 °C during 52 d following planting on 8 Apr. 2013; (1.8 × °C) + 32 = °F.
Citation: HortTechnology hortte 31, 1; 10.21273/HORTTECH04653-20
Slope estimates for grass cover per unit day and per unit °C indicate the capacity to establish over the time course from 10% to 90% grass cover (Table 2). Creeping bentgrass species averaged 6.5% grass cover per day, which was statistically better than velvet bentgrass cultivars (5.4%/d) but equal to colonial bentgrass (6.1%/d). Creeping bentgrass cultivars 13-M (8.7%/d) and Memorial (9.6%/d) were statistically equal to Barbeta perennial ryegrass (7.8%/d) in their capacity to achieve faster cover from 10% to 90%. Creeping bentgrass cultivars 007, Declaration, L-93, and T-1, along with all velvet bentgrass cultivars (Greenwich, SR-7200, and Villa) and Tiger II colonial bentgrass, were among the slowest to establish (less grass cover per day) over the time course from 10% to 90% grass cover.
Regression slope estimates for grass cover per unit day and cover per unit °C were highly correlated (r = 0.821, P ≤ 0.001). Perennial ryegrass during soil warming for the period from 10% to 90% grass cover achieved the highest grass cover per unit °C of 53.5%. Creeping bentgrass cultivars 13-M and Memorial, along with Capri colonial bentgrass, achieved statistically similar rates of increase in grass cover per unit °C and were comparable to perennial ryegrass (Table 2). Creeping bentgrass cultivar Declaration was the lowest in its capacity to increase grass cover during soil warming in the early spring period (28.6%/°C), which was about half the rate of perennial ryegrass. Similarly, all velvet bentgrass cultivars, along with some creeping bentgrass cultivars (007, L-93, and T-1) and ‘Tiger II’ colonial bentgrass, were statistically equal to ‘Declaration’ creeping bentgrass in their inability to achieve grass cover with soil warming in the early spring.
Even though bentgrass species and cultivars varied only 2 to 3 d in their initial seedling emergence (Table 2), days to 10%, 50%, and 90% cover ranged from 5.3 to 10.8 d (5.5 d difference), 12.4 to 17.5 d (5.1 d difference), and 17.8 to 26.4 d (8.6 d difference), respectively (Table 2). Colonial bentgrass cultivars averaged the fewest days to achieve 10%, 50%, and 90% grass cover, with velvet bentgrass cultivars on average requiring more time (days) to establish 10%, 50%, and 90% grass cover (Table 2). Bentgrass cultivars that were statistically equivalent to perennial ryegrass in days to 90% cover (16.4 d) included Capri and Tiger II colonial bentgrasses and most creeping bentgrasses cultivars except Declaration and L-93. None of the three velvet bentgrass entries were comparable to perennial ryegrass. Similar results among bentgrass species and cultivars were observed in time (days) to establish to 50% grass cover.
Soil temperatures to achieve 10%, 50%, and 90% cover are also reported in Table 2. Grass cover achieved at lower soil temperatures is beneficial for establishing in early spring with incremental soil warming as shown in Fig. 1. Perennial ryegrass achieved 10%, 50%, and 90% grass cover at lower soil temperatures corresponding to 10.3, 11.0, and 11.7 °C, respectively (Table 2). Perennial ryegrass has been shown to exhibit lower Tb for initial germination than bentgrass species (Trudgill et al., 2000), with Tb for perennial ryegrass reported to be as low as 1.4 °C (Moot et al., 2000). Moreover, perennial ryegrass has among the lowest GDD to 50% of final germination (Larsen and Bibby, 2005). Species averages indicated that velvet bentgrass entries exhibited the highest soil temperatures to achieve 10%, 50%, and 90% cover corresponding to 11.3, 12.5, and 13.6 °C. Velvet bentgrass soil temperatures for establishment are ≈1.0 to 2.0 °C higher than perennial ryegrass, and higher when compared with both creeping and colonial bentgrasses. The lowest soil temperature to achieve 90% grass cover equivalent to perennial ryegrass was ‘13-M’ and ‘Penncross’ creeping bentgrasses and ‘Capri’ colonial bentgrass, which were almost 1.0 °C higher than perennial ryegrass and close to 12.5 °C soil temperature. A similar soil temperature average of 12.5 °C—that was sufficient for 90% cover in some creeping and colonial bentgrasses—was required for velvet bentgrass to establish to only 50% grass cover (Table 2). Incremental differences as small as 1.0 °C soil temperature can have significant effects on grass cover, as indicated by slope estimates (grass cover per °C) shown in Table 2.
Table 3 displays periodic cover during the establishment period, with grass cover measured using the grid intersect method and as NDVI reflectance. All plots were at least 90% cover by 21 May and 95% cover by 25 May (data not shown). At all evaluation dates, bentgrass species and cultivars were statistically significant, except for the first rating date for NDVI (17 Apr.). Correlations between grass cover and NDVI were highly correlated, especially when grass cover and NDVI measurements are compared at similar times (data not shown).
Grass cover among bentgrass species and cultivars following planting on 8 Apr. 2013. Cover was determined using the intersect grid (cover) and normalized difference vegetation index (NDVI) methods. Grass cover during establishment was recorded on a 2- to 6-d interval until 29 May 2013.


Perennial ryegrass was observed in the top statistical performance group nine times according to the TPI for grass cover and NDVI, followed by ‘Penncross’ creeping bentgrass and ‘Capri’ colonial bentgrass with a TPI of six (Table 3). Creeping bentgrass cultivars 13-M and Memorial were reported to be in the top statistical performance group two times, with both 007 and T-1 creeping bentgrasses in the top statistical grouping only one time. No velvet bentgrass cultivar was ever observed to be in the top statistical performance group, along with ‘Declaration’ and ‘L-93’ creeping bentgrass and ‘Tiger II’ colonial bentgrass (Table 3).
Heineck et al. (2018) found ‘Declaration’ creeping bentgrass to have among the best seed germination rates for early spring laboratory test temperatures (mid-April) in their simulation test temperature of 7.0 °C. Our field study indicated that ‘Declaration’ was a poor performer, requiring higher soil temperatures to achieve 90% grass cover during soil warming in early spring along with the lowest grass cover per day (4.5%/d) and the lowest grass cover per °C (28.6%/°C) (Table 2). Alternatively, ‘Memorial’ creeping bentgrass in our field study performed well in terms of grass cover (Table 3), higher grass cover per day, and higher grass cover per °C (Table 2). In laboratory simulation tests Heineck et al. (2018) concluded ‘Memorial’ should not be recommended for planting in early spring because of poor germination characteristics at 7.0 °C. These results underscore the need to validate, in the field, simulation test temperatures conducted in the laboratory, as suggested by the work of Hardegree and Van Vactor (2000) because of the numerous biological, chemical, and physiological factors affecting establishment in the field (Egli and TeKrony, 1996; Hegarty, 1973; Weaich et al., 1996). A major shortcoming of this current field experiment is the study was not replicated in other years, and only one planting date was used—whereas multiple years of testing, along with multiple planting dates and locations (soil types), can provide more robust and reliable results and conclusions (Hardegree and Van Vactor, 2000). In addition, we did not evaluate different seed lots of bentgrass species and cultivars. Variation in seed lots are known to explain, in part, seed vigor and quality between cultivars (Larsen and Bibby, 2004; Liu et al., 2001). The use of more than one seed lot per cultivar may provide more reliable cultivar differences and results.
Cumulative soil temperature averages were also calculated and analyzed (Table 4). Cumulative soil temperature followed a near linear trend with days (Fig. 2). Perennial ryegrass exhibited among the lowest cumulative soil temperatures to establish to 10%, 50%, and 90% grass cover (Table 4). Colonial bentgrass was consistently among the lowest in cumulative soil temperatures, with velvet bentgrass cultivars requiring statistically higher cumulative soil temperatures to establish (Table 4). Bentgrass cultivars that were able to establish 50% to 90% grass cover at statistically equivalent cumulative soil temperatures to perennial ryegrass included Capri and Tiger II colonial bentgrasses, as well as 007, 13-M, and Memorial creeping bentgrasses (Table 4).
Cumulative soil temperatures to achieve 10%, 50%, and 90% grass cover among bentgrass species and cultivars following planting on 8 Apr. 2013. Grass cover during establishment was recorded on a 2- to 6-d interval using an intersect grid until 29 May 2013.



Cumulative (cum) daily soil temperature (temp) average recorded during the experimental period. Soil sensors were imbedded near the soil surface [1/2-inch (1.27-cm) soil depth] in unseeded check plots. Observed cumulative soil temperatures ranged from 2.7 °C (day 2) to 768.3 °C (day 52) following planting on 8 Apr. 2013. ‘Barbeta’ perennial ryegrass was the first to achieve 90% grass cover [day 16.4 (Table 2); cumulative soil temperature = 168.0 °C (Table 4)], while ‘SR-7200’ velvet bentgrass was the last to achieve 90% grass cover [day 26.4 (Table 2); cumulative soil temperature = 308.9 °C (Table 4)]; (1.8 × °C) + 32 = °F.
Citation: HortTechnology hortte 31, 1; 10.21273/HORTTECH04653-20

Cumulative (cum) daily soil temperature (temp) average recorded during the experimental period. Soil sensors were imbedded near the soil surface [1/2-inch (1.27-cm) soil depth] in unseeded check plots. Observed cumulative soil temperatures ranged from 2.7 °C (day 2) to 768.3 °C (day 52) following planting on 8 Apr. 2013. ‘Barbeta’ perennial ryegrass was the first to achieve 90% grass cover [day 16.4 (Table 2); cumulative soil temperature = 168.0 °C (Table 4)], while ‘SR-7200’ velvet bentgrass was the last to achieve 90% grass cover [day 26.4 (Table 2); cumulative soil temperature = 308.9 °C (Table 4)]; (1.8 × °C) + 32 = °F.
Citation: HortTechnology hortte 31, 1; 10.21273/HORTTECH04653-20
Cumulative (cum) daily soil temperature (temp) average recorded during the experimental period. Soil sensors were imbedded near the soil surface [1/2-inch (1.27-cm) soil depth] in unseeded check plots. Observed cumulative soil temperatures ranged from 2.7 °C (day 2) to 768.3 °C (day 52) following planting on 8 Apr. 2013. ‘Barbeta’ perennial ryegrass was the first to achieve 90% grass cover [day 16.4 (Table 2); cumulative soil temperature = 168.0 °C (Table 4)], while ‘SR-7200’ velvet bentgrass was the last to achieve 90% grass cover [day 26.4 (Table 2); cumulative soil temperature = 308.9 °C (Table 4)]; (1.8 × °C) + 32 = °F.
Citation: HortTechnology hortte 31, 1; 10.21273/HORTTECH04653-20
Cumulative soil temperatures captured at least 99% of the covariation in GDD0, GDD5, and GDD10 (Fig. 3). Linear regression models reported in Fig. 3 allow cumulative soil temperatures from Table 4 to be converted to GDD0, GDD5, and GDD10 for bentgrass species and cultivars. Base temperatures to initiate seed germination can vary with the species and cultivar (Beard, 1979; Larsen and Bibby, 2005; Trudgill et al., 2000). Therefore, adjusting cumulative soil temperatures to predict GDD using different Tb are presented here for this single planting date.

Relationship between cumulative soil temperatures and growing degree day (GDD) comparing GDD base soil temperatures (temp) of 0, 5, and 10 °C with cumulative (cum) daily soil temperature average recorded during the experimental period. Soil sensors were imbedded near the soil surface [1/2-inch (1.27-cm) soil depth] in unseeded check plots. Observed cumulative soil temperatures ranged from 2.7 °C (GDD0 = 4.7 °C; GDD5 = −15.8 °C; GDD10 = −16.2 °C) to 768.3 °C (day 52, GDD0 = 808.6 °C; GDD5 = 541.6 °C; GDD10 = 326.3 °C) following planting on 8 Apr. 2013. Arrows indicate cumulative soil temperatures when grass cover (Table 3) was evaluated at 21 and 25 Apr., and 2, 8, and 13 May 2013; (1.8 × °C) + 32 = °F.
Citation: HortTechnology hortte 31, 1; 10.21273/HORTTECH04653-20

Relationship between cumulative soil temperatures and growing degree day (GDD) comparing GDD base soil temperatures (temp) of 0, 5, and 10 °C with cumulative (cum) daily soil temperature average recorded during the experimental period. Soil sensors were imbedded near the soil surface [1/2-inch (1.27-cm) soil depth] in unseeded check plots. Observed cumulative soil temperatures ranged from 2.7 °C (GDD0 = 4.7 °C; GDD5 = −15.8 °C; GDD10 = −16.2 °C) to 768.3 °C (day 52, GDD0 = 808.6 °C; GDD5 = 541.6 °C; GDD10 = 326.3 °C) following planting on 8 Apr. 2013. Arrows indicate cumulative soil temperatures when grass cover (Table 3) was evaluated at 21 and 25 Apr., and 2, 8, and 13 May 2013; (1.8 × °C) + 32 = °F.
Citation: HortTechnology hortte 31, 1; 10.21273/HORTTECH04653-20
Relationship between cumulative soil temperatures and growing degree day (GDD) comparing GDD base soil temperatures (temp) of 0, 5, and 10 °C with cumulative (cum) daily soil temperature average recorded during the experimental period. Soil sensors were imbedded near the soil surface [1/2-inch (1.27-cm) soil depth] in unseeded check plots. Observed cumulative soil temperatures ranged from 2.7 °C (GDD0 = 4.7 °C; GDD5 = −15.8 °C; GDD10 = −16.2 °C) to 768.3 °C (day 52, GDD0 = 808.6 °C; GDD5 = 541.6 °C; GDD10 = 326.3 °C) following planting on 8 Apr. 2013. Arrows indicate cumulative soil temperatures when grass cover (Table 3) was evaluated at 21 and 25 Apr., and 2, 8, and 13 May 2013; (1.8 × °C) + 32 = °F.
Citation: HortTechnology hortte 31, 1; 10.21273/HORTTECH04653-20
The rate of cover per unit day and per unit °C increased with decreasing cumulative soil temperature during soil warming in early spring (Table 5). Bentgrass species and cultivars to establish cover from 50% to 90% were closely associated with the capacity of bentgrass species to establish cover at lower cumulative soil temperatures (Table 4). Fewer days to establish cover (i.e., faster establishment) were generally associated with lower cumulative soil temperatures. The capacity of bentgrass species to establish cover under lower cumulative soil temperatures during early spring (Figs. 1 and 2) were associated with faster rates of establishment.
Selected correlation values for seed weight, percent grass cover per day (Cover/d), and percent grass cover per °C (Cover/°C) with cumulative soil temperatures to achieve 10%, 50%, and 90% cover for bentgrass species and cultivars (n = 39). Grass cover among bentgrass species and cultivars was determined using the intersect grid following planting on 8 Apr. 2013 and recorded on a 2- to 6-d interval until 29 May 2013.


During establishment, seed vigor and seed quality are more closely related to the early stages of establishment (seed germination and emergence). Alternatively, at later stages during development of mature plants and the formation of dense turf, establishment is under genetic control. A positive relationship is often observed between seed weight or size and laboratory seed germination percentages (Brown, 1977; Larsen and Andreasen, 2004; Veronesi et al., 1983). It is acknowledged that within a species, larger seeds are more vigorous but larger seeds have lower seed counts per unit area when planted by weight in the field. Therefore, seed size and its relationship to field emergence and establishment is more complicated. In our study, bentgrass species and cultivars of larger seed size or weight (Table 1) were positively correlated with greater establishment cover during early stages of establishment (Table 6). For example, r-values ranged from 0.462 (P = 0.01, n = 39) measured on 21 Apr. to 0.254 (P > 0.05) on 13 May (Table 6). Similarly, larger seed weights were associated with fewer days to 10% cover (r = −0.376, P = 0.024, n = 39), but seed size and weight were uncorrelated with later stages of establishment (time to 50% and 90% cover). Conversely, Christians et al. (1979) reported higher seed counts (lighter seed weights) among kentucky bluegrass cultivars to establish stands more rapidly than cultivars with fewer seeds per gram (heavier seed weights), when seeded at the same rate of 73 kg·ha−1. They also found that differences due to seeding rate, comparing seed weight per unit area vs. seed count per unit area, exist only during the initial stages of establishment (within 6 months after planting). Therefore, in our study, seeding rates were standardized to deliver the same live seed count per unit area (31,000 seeds/m2), using different seeding rates (Table 1) to account for seed size differences and their potential impact on cover during the early stages of establishment.
Selected correlation values for bentgrass species and cultivars (n = 39) with grass cover following planting on 8 Apr. 2013. Grass cover among bentgrass species and cultivars was determined on a 2- to 6-d interval until 29 May 2013.


Slope estimates measured as grass cover per day and grass cover per °C were positively correlated with cover measured using the intersect grid and NDVI reflectance (Table 6). Predicted time (days) to 10%, 50%, and 90% grass cover were inversely related to cover and NDVI, indicating shorter intervals (days) were associated with greater cover and NDVI reflectance. Days to 50% and 90% cover were more strongly correlated with cover and NDVI measured during later stages of establishment (Table 6).
Overall, all velvet bentgrass cultivars evaluated required higher soil temperatures (13.6 °C) to establish to 90% cover during soil warming in early spring. Velvet bentgrasses were slow to establish during this period, requiring 26 d after seedling emergence to establish to 90% cover. ‘Barbeta’ perennial ryegrass was able to establish 90% cover at 16 d after seedling emergence, which corresponded to soil temperatures of 11.6 °C. Creeping bentgrass cultivars 007, 13-M, and Memorial, along with colonial bentgrass cultivars Capri and Tiger II, were statistically equal to Barbeta perennial ryegrass in their capacity after seedling emergence to achieve faster cover at lower soil temperatures. Bentgrass species and cultivars varied only 2 to 3 d in their initial seedling emergence, while time (days) varied among bentgrasses from 5.5 d to 10% cover to 8.6 d to 90% cover. Heavier (larger) bentgrass seed was generally associated with faster cover during the early stages of establishment (to 10% cover), but seed size was uncorrelated with establishment during later stages from 50% to 90% cover. Most bentgrass species and cultivars emerged at ≈10 °C soil temperature. Therefore, seeding as early as possible when soil temperatures are 10 °C and higher could be recommended for bentgrass species and cultivars that have been field-evaluated for superior cold-temperature germination and emergence characteristics. Future research should focus on soil temperature and seed establishment vigor using multiple planting sites and seeding dates.
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