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Boron fertilization of bentgrass.

BORON, AN ESSENTIAL TRACE ELEMENT, is often applied to agricultural and horticultural crops. The exact function of B in the plant is not fully understood (Blevins and Lukaszewski, 1998), but it does appear to play a critical role in cell wall structure (Hull, 2002). Boron fertilizer recommendations include foliar or soil-applied B for alfalfa (Medicago sativa L.), cole crops, cotton (Gossypium hirsutum L.), peanuts (Arachis hypogaea L.), and fruit trees at rates ranging from 0.4 to 3.4 kg B [ha.sup.-1] (Adams et al., 1994; Guertal et al., 1998). Research has shown that B responses to foliar or soil-applied B are common in some field crops. For example, foliar application of B at rates of 0.3 to 1.3 kg B [ha.sup.-1] increased yield or seed weight of soybean (Glycine max L.) and cotton (Gascho, 1993; Oplinger et al., 1993).

Grass response to B fertilization has been less well documented. Greenhouse studies have examined the growth response of Kentucky bluegrass (Poa pratensis L.), creeping bentgrass, and tall fescue (Festuca arundinacea Schreb.). Addition of B at rates of 0.8 or 4.8 mg [kg.sup.-1] was not detrimental to germination and establishment, as germination of Kentucky bluegrass and creeping bentgrass increased 15 to 20% when compared with zero-B control treatments (Oertli et al., 1961). Tall fescue, creeping bentgrass, Kentucky bluegrass, perennial ryegrass (Lolium perenne L.), bermudagrass [Cynodon dactylon (L.) Pers.], and zoysiagrass (Zoysia japonica Steud.) were grown in nutrient solution containing 10 mg [kg.sup.-1] B. Leaf tip burn due to B toxicity was observed, with greater injury occurring on the cool season grasses. However, even with high concentrations of plant B, little decline in plant vigor was observed, and frequent clipping removed most visible tip necrosis (Oertli et al., 1961). In another greenhouse study, Kentucky bluegrass maintained at high or low levels of general fertility was fertilized with B at rates of 1.7 or 8.4 kg B [ha.sup.-1]. In the low-fertility plots, bluegrass receiving supplemental B had increased color, growth, and dry matter yield when compared with plots receiving no B (Deal and Engel, 1965). In the high-fertility plots, application of 8.4 kg B [ha.sup.-1] increased turf growth during the first 6 wk of the study, but did not affect growth for the remaining 7 wk of the study. All growth effects were most pronounced in the first 5 wk of the study, and in later weeks, tip burn of leaves was observed, similar to the study of Oertli et al. (1961). It was concluded that in turf with low fertility, the 1.7 kg B [ha.sup-1] rate temporarily increased turf green color, while in well-fertilized turf the 8.4 kg B [ha.sup.-1] rate was toxic, when examined during the entire 13 wk of the study (Deal and Engel, 1965).

Boron fertilization research with warm-season grasses has largely focused on forage-type bermudagrass. The 3-yr average yield of Coastal bermudagrass was increased by the yearly application of B at 2.2 kg B [ha.sup.-1] (Spooner and Huneycutt, 1983). In another field study, B was applied yearly at 0, 1.1, 2.2, or 4.4 kg B [ha.sup.-1] to seven different bermudagrass cultivars. When averaged across all grasses, dry matter yield was increased when B was applied at 2.2 kg [ha.sup.-1]. However, the effect was significant in only two of seven cultivars. It was concluded that the variable data collected from the 4-yr study would not support a general recommendation of supplemental B on forage-type bermudagrasses (Monson and Gaines, 1986).

Of the B research conducted with turfgasses, none of the published work was conducted under field conditions (Oertli et al., 1961; Deal and Engel, 1965; Lee et al., 1996). Typically, B toxicity symptoms were most evident at higher rates of B fertilization, when grasses were grown in a B-amended nutrient solution (Oertli et al., 1961; Lee et al., 1996). Positive growth responses were observed at lower rates of B fertilization in soil or soil/peat mixes, especially if background soil fertility was also low (Deal and Engel, 1965).

Boron will leach in sandy soils (Hull, 2002), and possible downward movement in sand-based putting greens could affect B fertilization needs for turf. There is no data examining B fertilization of putting greens in field situations, and no research which examines B fertilization of recently introduced bentgrass cultivars. Moreover, micronutrient fertilization is a growing marketing tool in the turf industry, and additional data about micronutrient fertilization of turf is needed to help golf course superintendents decide if supplemental B fertilization is necessary. The objective of this research was to examine the effect of B fertilization on quality, shoot density, and rooting of cultivars of creeping bentgrass in both a greenhouse and field study.

MATERIALS AND METHODS

Greenhouse Experiment

In December 1998 a greenhouse experiment was initiated at the Plant Science Research Center, Auburn, AL. Three creeping bentgrass cultivars ('SR1020', 'Crenshaw', and 'Dominant') were seeded into 2.5-cm-diam. conetainers filled with a 15% reed sedge peat/85% sand greensmix to an approximate bulk density of 1.5 g [cm.sup.-3]. When the bentgrass seedlings were [approximately equal to] 3 wk old, seedlings in the conetainers were thinned to one seedling per conetainer. To lessen experimental variability, an experimental unit was the average of data collected from a single row of 10 individual conetainers. This average was considered one replication of a cultivar/B rate treatment combination. Cultivar/B rate treatments were arranged in the greenhouse in a completely randomized design. There were four replications of each bentgrass cultivar/B rate treatment. Thus, with three bentgrass cultivars and 5 B rates there were 15 treatments in the study, each replicated four times, a total of 600 conetainers in the study.

Boron treatments were weekly applications of B (Boric acid, [H.sub.3]B[O.sub.3]) applied at 0.0, 0.5, 1.0, 2.0, and 3.0 mg [kg.sup.-1] B. Boron treatments were applied weekly in 30 mL (per conetainer) of a B-depleted Hoaglands solution, starting immediately after the conetainers were thinned to one seedling (3 wk of growth). Seedlings were maintained for an additional 8 wk, after which aboveground shoot growth was removed. Wet and dry weight of shoot growth was determined. Harvested roots were washed though a sieve to remove sand and peat, and dry weight determined.

Field Study

Beginning in March 1999, a field study was initiated at the Auburn University Turfgrass Research Unit on a native soil (Marvyn loamy sand; fine-loamy, kaolinitic, thermic Typic Kanhapludult) bentgrass putting green. The green had been established in the fall of 1997 with four replicate blocks of the creeping bentgrass cultivars: 'Penn G2', 'L-93', 'Crenshaw', 'Penncross', 'Penn A2', 'Penn G6', 'Penn G1', 'SR1020', and 'Dominant'. Each bentgrass cultivar main block was 3.7 by 2.1 m in size. Cultivar main blocks were split into four strips of 0.9 by 2.1 m, each receiving one of four yearly B fertilizer rates (0, 0.55, 1.1, or 2.2 kg B [ha.sup.-1] [yr.sup.-1]), split into 12 monthly applications. Boron source was sodium borate (Solubor, 20.5% B, U.S. Borax, Inc., Valencia, CA). Boron treatments were applied with a backpack C[O.sub.2]--powered sprayer in a 468 L [ha.sup.-1] spray volume. Boron was applied at the beginning of each month beginning in March 1999 and continued until June 2001.

The research area was maintained uniformly as a bentgrass putting green with all plots mowed daily at a height of 4 mm using a triplex greens mower. Additional plot maintenance included vertical mowing (2.5-cm depth) and topdressing during the months of September, December, and February, and high-pressure water injection during the months of May, June, and July. Plots were core aerified (10-mm-diam. hollow tine) and sand topdressed in October of each year, with cores removed. Fertilizer was applied with B-depleted materials (N[H.sub.4]N[O.sub.3], 34-0-0; triple super phosphate, 0-46-0; [K.sub.2]S[O.sub.4], 0-0-50) to supply N at 0.01 g [m.sup.-2] [mo.sup.-1], and P and K were applied according to soil-test recommendations (taken four times each year). Typical yearly soil tests for the research area reported soil-test P at 112 kg [P.sub.2][O.sub.5] [ha.sup.-1] (very high), K at 170 kg [K.sub.2]O [ha.sup.-1] (high), and a pH of 6.2. Irrigation was applied as needed to supply 2.5 cm water per week.

Collected data included monthly clipping yield and relative turf quality. Clipping data was obtained by mowing a 0.45-by 2-m strip in the middle of each plot, drying the clippings in a forced-air oven for 48 h, and recording dry weight. Relative turf color was recorded on a 1- to 9- scale, with a score of 1 being brown turf, a 9 dark green, and a 5 as a satisfactory green color. In June of 2000 and 2001, a subsample of collected clippings was dry-ashed, extracted, and analyzed for B content via ICP (inductively coupled plasma emission spectroscopy) analysis (Adams et al., 1994). In June 2000 and 2001, five 2.5-cm-diam. plugs were removed randomly from each plot, and compressed thatch depth was recorded. An average thatch depth for each plot was obtained by averaging the five subsamples. In June 2001, an additional five 2.54-cm-diam. turf plugs were removed from the control (0 B), low (0.55 kg B), and high (2.2 kg B) treatments. Individual shoots from these samples were separated and counted to obtain shoot density readings for each sample. The five subsamples were averaged and reported as an average shoot density for each plot.

RESULTS AND DISCUSSION

Greenhouse Experiment

There was not a significant B rate x bentgrass cultivar interaction for wet or dry weight of bentgrass shoots. The main effect of cultivar was significant, with both wet and dry weights of bentgrass shoots varying because of cultivar. The average wet and dry weight of Dominant was 1.33 and 0.41 g per conetainer, respectively, significantly greater than the shoot weights of Crenshaw (1.19 and 0.37 g, wet and dry, respectively) or SR-1020 (1.13 and 0.33 g). There was no difference in shoot wet or dry weight of Crenshaw or SR-1020. Dry root weight of the bentgrass cultivars was unaffected by cultivar.

As B rate increased, the dry weight of bentgrass shoots increased (Fig. 1). Although not significant, shoot wet weight followed a similar trend with wet weight increasing as B rate increased, but variability within treatments was high and the regression equation was not significant. Root dry weight was opposite the trend observed with shoot weights, as root weight generally decreased as B rate increased. However, this relationship was not significant, as determined by linear regression (Fig. 1). Root dry weight was greatest at the 0.5 mg [kg.sup.-1] B rate, and decreased thereafter as B rate increased.

[FIGURE 1 OMITTED]

Increases in dry matter production due to B application have been observed in Kentucky bluegrass (Deal and Engel, 1965) and forage bermudagrass production (Monson and Gaines, 1986). In a greenhouse study of micronutrient toxicity in Kentucky bluegrass, B rates from 5.4 to 10.8 mg [kg.sup.-1] B did not affect dry weight of bluegrass shoots, although B toxicity symptoms were apparent at the lowest rate of 5.4 mg [kg.sup.-1] B. As B concentrations increased from 21.6 to 129.7 mg [kg.sup.-1] B, shoot weight of Kentucky bluegrass decreased (Lee et al., 1996). In our study there were no visible signs of B toxicity on the leaf tips of the bentgrass, as the lower B concentrations applied may not have created toxic conditions. Increases in dry matter production at lower rates of B addition may have been missed in the study by Lee et al., as their lowest B rate was similar to the highest rates used in this study.

Field Experiment

Boron fertilizer rates used in this study (0 to 2.2 kg B [ha.sup.-1]) were based on B experiments previously published. For example, Monson and Gaines (1986), in a similar geographic region, used rates of 0 to 4.4 kg B [ha.sup.-1] for their forage bermudagrass study. Other cool season turfgrass research used a B rate of 1.7 kg B [ha.sup.-1] (Deal and Engel, 1965). Last, the selected B rates bracket B recommendations (0.56 to 1.7 kg B [ha.sup.-1]) for B-responsive crops in Alabama (Adams et al., 1994).

Clipping Production

There were 16 separate clipping collections taken during the 2 yr of the study. At no time was there a significant B rate x cultivar interaction, and at no time did the rate of B fertilization affect dry weight of clippings (Table 1). This differs from that observed in the greenhouse trial, where dry shoot growth increased as B rate increased. The field study was conducted on a loamy sand soil (80% sand) with a sand content equal to that found in many sand/peat-based putting greens. However, the clay and organic matter content of the native soil green may have reduced the likelihood of a B response.

In other field research, application of B at 8.4 kg [ha.sup.-1] increased dry matter production for the first 6 wk of the study (Deal and Engel, 1965). During Weeks 7 though 13 of the study, however, signs of B toxicity were evident and turf growth was reduced. Thus, the long-term application of B at 8.4 kg [ha.sup.-1] was toxic to the Kentucky bluegrass turf. In a nutrient solution study, dry matter production of Kentucky bluegrass was reduced at B rates > 2 mM B (21.6 mg [L.sup.-1]) (Lee et al., 1996). In another field study, application of B at 2.2 kg [ha.sup.-1] [yr.sup.-1] increased dry matter production in bermudagrass (Monson and Gaines, 1986).

Clipping yield was affected by bentgrass cultivar (Table 1). On 10 of 16 sampling dates Penncross had among the highest clipping yields, and on 6 of those 10 dates Penncross had a significantly higher yield than any other cultivar. Penncross is usually considered a heat-sensitive cultivar, and has been shown to be a bentgrass cultivar with a lower root-to-shoot ratio than heat-tolerant cultivars (Schlossberg and Karnok, 2001; Xu and Huang, 2001). In an extreme heat-stress environment such as central Alabama, it may be that heat-tolerant cultivars such as Crenshaw, SR-1020, or L-93 survive heat by producing less topgrowth and more roots. Penncross may simply continue to produce more clippings throughout the year, as its survival mechanism for heat-stress does not include increased root production. On 10 of 16 sampling dates the heat-tolerant cultivar L-93 (Xu and Huang, 2001) had a lower clipping yield than the heat-sensitive Penncross, possibly because the resources of L-93 had shifted to root production.

Bentgrass cultivars with documented high shoot density (Penn A-2, Penn G-1, Penn G-2, and Penn G-6; [Sweeney et al., 2001]) did not always produce a greater clipping yield than those cultivars considered to have standard shoot densities (Penncross, Crenshaw, and SR-1020; [Sweeney et al., 2001]). Clipping yield of any of the Penn cultivars were similar to each other and to other bentgrass cultivars in the study. With the exception of the Penncross differences discussed above, differences in clipping yield due to cultivar were relatively minor, and varied from sampling to sampling.

Thatch Depth and Shoot Density

No significant B rate x cultivar interaction was observed for thatch depth, nor did the main effect of B rate significantly affect thatch depth (Table 2). There were differences in thatch depth due to cultivar, as cultivars with a higher shoot density (Penn A-2, Penn G-1, Penn G-6) had a greater thatch depth than other cultivars. Penncross, considered a low-shoot density cultivar, had the lowest level of thatch in June 2000, and was one of three cultivars with a low thatch depth in June 2001 (others were Penn G-2 and SR-1020).

Collected shoot data matched the thatch data, as cultivars with the greatest thatch also had the highest shoot density (Penn A-2, Penn G-1, and Penn G-6), and those with lowest thatch had lowest shoot density (Penncross). Shoot density was unaffected by 2 yr of B application, and there was not a significant B rate x cultivar interaction (Table 2). It is not uncommon for Penncross to have low shoot densities, and this result has been shown in other work (Schlossberg and Karnok, 2001; Sweeney et al., 2001).

Boron Concentration and Uptake

There was never a significant B rate x cultivar interaction for B concentration or uptake in either year of the study. In June 2000, B concentration in harvested bentgrass clippings increased quadratically as B rate increased, maximizing at a B application rate of 1.6 kg B [ha.sup.-1] (Table 3). Boron content of harvested bentgrass was unaffected by B rate in 2001. Previous work with B uptake has shown some increase in B concentration in harvested forage with increased rates of B fertilization, but there was no correlation between B concentration and yield (Monson and Gaines, 1986). Another study that examined B uptake by bermudagrass ('Tifway II') used boric acid treated recycled paper as the B source (Wilkinson, 1997). No visual symptoms of B toxicity were observed, and B recovery in plant growth was small (Wilkinson, 1997).

In both years of the study, B concentration in plant tissue was unaffected by cultivar (Table 3). There were differences in B uptake due to cultivar, with the cultivar Penncross having significantly greater B uptake than other cultivars in both years of the study. In both June 2000 and 2001 Penncross had the greatest dry matter production (Table 1), which reflected greater B uptake in those same months.

Turf Color

Monthly color ratings never contained a significant cultivar x B rate interaction, and the main effect of B rate never affected bentgrass color (data not shown). The bentgrass did not demonstrate positive (darker green color) or negative (toxicity symptoms) effects due to B applications. This lack of color response and/or toxicity symptoms has been reported in other field studies, even with rates far higher than applied in this study (Wilkinson, 1997).

There were differences in bentgrass color due to cultivar (data not shown). The most consistent effect was that Penncross had significantly lower color ratings than other cultivars in the study. For example, in June 1999 Penncross received a relative color score of 4.6, significantly lower than the average color score of 6.5 for the other eight cultivars. In April 2000, Penncross received a score of 5.9, significantly lower than the average score of 6.8 for the remaining cultivars. No one cultivar exhibited better color than another throughout the 2 yr of the study. Typically, the cultivar Penn A-2 received the highest color rating, but this was not always significantly better than others.

CONCLUSIONS

Application of B fertilizer at rates up to 4.4 kg B [ha.sup.-1] did not affect dry matter production, thatch depth, or shoot density of eight different bentgrass cultivars grown in a loamy sand putting green. In the greenhouse study, shoot dry weight increased as B rate increased. In the field (in one year only), B concentration in bentgrass increased as B rate increased. At the B rates used in this study there were no visual impacts on turf color, and there was no evidence of B toxicity. Results from this study indicate that B fertilization of bentgrass grown on a native soil (loamy sand) putting green did not produce any improvement in color, shoot density, or dry matter production. Boron fertilization of turfgrasses maintained on United States Golf Association-type (high sand) greens might warrant further research.
Table 1. Dry matter production of creeping bentgrass as affected by
B rate and cultivar, Auburn, AL, 1999-2001.

                              June         July     Aug.    Sept.
                              1999         1999     1999    1999

                                          g [m.sup.-2]

B rate, kg [ha.sup.-1]

  0.0                         16.6          9.8      3.9     7.3
  0.5                         17.7          9.1      4.2     7.1
  1.0                         16.9          8.5      4.0     7.1
  2.0                         17.8          9.8      4.1     7.0
  Linear ([dagger])            ns           ns       ns      ns
  Quadratic                    ns           ns       ns      ns
Cultivar
  A-2                    21.9a ([double   10.7ab    3.3c    6.4cd
                               dagger])
  G-1                    21.3a            11.7a     3.7bc   7.0bc
  G-6                    16.3bcd          10.2abc   3.9bc   5.5d
  L-93                   19.4ab            9.6abc   4.1bc   7.2bc
  SR-1020                l6.1bcd           9.7abc   4.6ab   8.1ab
  Dominant               17.2bc            8.7abc   4.4ab   7.4bc
  Crenshaw               16.1bcd           8.3bc    3.6c    6.6cd
  G-2                    14.6cd            7.2c     3.6c    7.2bc
  Penncross              12.6d             7.4bc    5.1a    8.8a

                          Oct.     Feb.     Mar.    Apr.     May
                          1999     2000     2000    2000     2000

                                           g [m.sup.-2]

B rate, kg [ha.sup.-1]

  0.0                     11.1     11.5     13.6     7.5     10.3
  0.5                     11.4     11.2     13.4     8.0     10.2
  1.0                     11.8     12.0     13.5     8.2     10.4
  2.0                     11.6     12.2     13.7     8.2     10.3
  Linear ([dagger])        ns       ns       ns      ns       ns
  Quadratic                ns       ns       ns      ns       ns
Cultivar
  A-2                     9.6c      9.5a   11.3c    7.1c     8.8d
  G-1                    12.4a     11.7a   13.8ab   7.4c     9.3cd
  G-6                    10.4bc    10.8a   14.3ab   8.7b    10.26c
  L-93                   11.4ab    10.6a   13.6ab   7.4c    10.5b
  SR-1020                11.1a     11.1a   13.5ab   7.8bc   l0.0bc
  Dominant               11.2a     10.4a   15.1a    8.2bc   ll.1ab
  Crenshaw               10.8abc    9.6a   11.9b    7.7bc   10.5b
  G-2                    12.0ab     9.5a   13.3b    7.8bc   10.3bc
  Penncross              11.8ab    11.4a   13.8ab   9.7a    10.7a

                         June    Aug.    Sept.     Oct.
                         2000    2000     2000     2000

                                g [m.sup.-2]

B rate, kg [ha.sup.-1]

  0.0                    5.9     10.2     17.7     10.0
  0.5                    5.9     10.0     17.6     10.1
  1.0                    6.4     10.1     17.6     10.1
  2.0                    6.1     10.2     17.4     10.2
  Linear ([dagger])       ns      ns       ns       ns
  Quadratic               ns      ns       ns       ns
Cultivar
  A-2                    5.7b    9.1c    18.2bc    8.9bc
  G-1                    5.2b    9.7bc   14.4d     9.5b
  G-6                    6.1b   10.3b    20.2a     8.5bc
  L-93                   6.0b   10.4b    18.0bc    8.8bc
  SR-1020                6.1b   10.4b    16.6cd    9.2bc
  Dominant               5.8b   10.6b    19.1ab    9.1bc
  Crenshaw               5.5b    9.6bc   16.7cd    7.5c
  G-2                    5.9b    9.5bc   14.7cd    9.1bc
  Penncross              8.2a    11.7a   17.0cd   11.3a

                          Nov.    Dec.    June
                          2000    2000    2001

                               g [m.sup.-2]

B rate, kg [ha.sup.-1]

  0.0                     10.7     6.8     6.7
  0.5                     10.8     7.1     7.5
  1.0                     11.5     6.9     7.2
  2.0                     11.2     6.8     7.5
  Linear ([dagger])        ns      ns      ns
  Quadratic                ns      ns      ns
Cultivar
  A-2                     9.2bc   4.7c    5.6d
  G-1                     8.4c    5.9b    5.5d
  G-6                     9.9bc   4.8c    5.6d
  L-93                    9.6bc   6.2b    5.8d
  SR-1020                10.0b    6.7ab   6.1cd
  Dominant                9.8bc   7.1a    7.3bc
  Crenshaw                9.7bc   6.0b    6.1cd
  G-2                    10.3b    7.2a    7.5b
  Penncross              12.7a    7.2a    9.1a

([dagger]) Significance of regression equations fit to the data;
ns, not significant.

([double dagger]) Within each sampling date, means separation by
Duncan's Mean Separation, [alpha] = 0.05.

Table 2. Thatch depth and shoot density of bentgrass as affected
by B rate and cultivar, June 2000 and 2001.

                              Thatch depth

                           June          June     Shoot density
                           2000          2001       June 2001

                                                     shoots
                                   mm              [cm.sup.2]

B rate, kg
    [ha.sup.-1]
    [yr.sup.-1]
  0.0               32.6                 41.1        6.3
  0.5               33.2                 41.3        6.3
  1.0               32.5                 41.4         na ([dagger])
  2.0               32.8                 41.3        6.2
  Linear ([double    ns                   ns          ns
    dagger])
  Quadratic          ns                   ns          ns
Cultivar
  Penn A-2          34.6ab ([section])   43.6a        7.0a
  Penn G-1          35.6a                44.3a        6.8ab
  Penn G-6          36.3a                44.1a        7.0a
  L-93              32.2cd               40.8b        5.7d
  SR-1020           31.0d                39.2bc       6.4bc
  Dominant          33.4bc               41.1b        6.1cd
  Crenshaw          32.5cd               41.3b        6.0cd
  Penn G-2          30.6d                38.1c        6.3c
  Penncross         28.5e                38.5c        5.1e

([dagger]) na, not available.

([double dagger]) Significance of regression equations
fit to the data; ns, not significant.

([section]) Within each sampling date, means separation by
Duncan's Mean Separation, [alpha] = 0.05.

Table 3. Boron concentration and uptake by bentgrass
cultivars as affected by B rate, June 2000 and 2001.

                                        June 2000

                                B uptake           Concentration

                              g [m.sup.-2]         ug [g.sup.-1]

B Rate, kg [ha.sup.-1]
  0.0                             0.04                 4.8
  0.5                             0.04                 4.9
  1.0                             0.04                 5.1
  2.0                             0.04                 5.0
  Linear ([dagger])                ns                   ns
  Quadratic                        ns                  0.007
Cultivar
  Penn A-2               0.03b ([double dagger])       5.2a
  Penn G-1               0.03b                         5.2a
  Penn G-6               0.04b                         4.8a
  L-93                   0.04b                         4.7a
  SR-1020                0.04b                         4.7a
  Dominant               0.03b                         4.9a
  Crenshaw               0.03b                         4.8a
  Penn G-2               0.04b                         5.Oa
  Penncross              0.07a                         5.3a

                                  June 2001

                           B uptake     Concentration

                         g [m.sup.-2]   ug [g.sup.-1]

B Rate, kg [ha.sup.-1]
  0.0                        0.05            8.7
  0.5                        0.06            9.5
  1.0                        0.05           10.0
  2.0                        0.06            9.9
  Linear ([dagger])           ns             ns
  Quadratic                   ns             ns
Cultivar
  Penn A-2                  0.04c            9.1a
  Penn G-1                  0.04c            9.8a
  Penn G-6                  0.04c           10.0a
  L-93                      0.04c           10.0a
  SR-1020                   0.05bc           9.0a
  Dominant                  0.07b            9.2a
  Crenshaw                  0.04c            9.4a
  Penn G-2                  0.07b            9.4a
  Penncross                 0.10a            9.8a

([dagger]) Significance of regression equations fit to the
data; as, not significant.

([double dagger]) Within each sampling date, means separation by
Duncan's Mean Separation, [alpha] = 0.115.


REFERENCES

Adams, J.F., C.C. Mitchell, and H.H. Bryant. 1994. Soil test fertilizer recommendations for Alabama crops. Agron. and Soils Dep. Series No. 178. Alabama Agric. Exp. Stn., Auburn Univ.

Blevins, D.G., and K.M. Lukaszewski. 1998. Boron in plant structure and function. Annu. Rev. Plant Physiol. Plant Mol. Biol. 49:481-500.

Deal, E.D., and R.E. Engel. 1965. Iron, manganese, boron and zinc: Effects on growth of Merion Kentucky bluegrass. Agron. J. 57:533-555.

Gascho, G.J. 1993. Boron and nitrogen applications to soybeans: Foliar and through sprinkler irrigation, p. 17-33. In D.D. Howard (ed.) Foliar fertilization of soybeans and cotton. PPI/FAR Tech. Bull. 1993-1. Potash and Phosphate Inst. and Foundation for Agron. Res., Norcross, GA.

Guertal, E.A., A.O. Abaye, B.M. Lippert, G.J. Gascho, and G.S. Miner. 1998. Boron uptake and concentration in cotton and soybean as affected by boron source. Commun. Soil Sci. Plant Anal. 29:3007-3014.

Hull, R.J. 2002. Recent research offers clues to boron's purpose. Turfgrass Trends 11:11-16.

Lee, C.W., M.B. Jackson, M.E. Duysen, T.P. Freeman, and J.R. Self. 1996. Induced micronutrient toxicity in 'Touchdown' Kentucky bluegrass. Crop Sci. 36:705-712.

Monson, W.G., and T.P. Gaines. 1986. Supplemental boron effects on yield and quality of seven bermudagrasses. Agron. J. 78:522-523.

Oertli, J.J., O.R. Lunt, and V.B. Youngner. 1961. Boron toxicity in several turfgrass species. Agron. J. 53:262-265.

Oplinger, E.S., R.G. Hoeft, J.W. Johnson, and P.W. Tracy. 1993. Boron fertilization of soybean: A regional summary. p. 7-16. In Foliar fertilization of soybeans and cotton. PPI/FAR Tech. Bull. 1993-1. Potash and Phosphate Inst. and Foundation for Agron. Res., Norcross, GA.

Schlossberg, M.J., and K.J. Karnok. 2001. Root and shoot performance of three creeping bentgrass cultivars as affected by nitrogen fertility. J. Plant Nutr. 24:535-548.

Spooner, A.E., and H. Huneycutt. 1983. Effects of boron on Coastal bermudagrass. Ark. Farm Res. 32(4):2.

Sweeney, P., K. Danneberger, D. Wang, and M. McBride. 2001. Root weight, nonstructural carbohydrate content and shoot density of high-density creeping bentgrass cultivars. HortScience 36:368-370.

Wilkinson. S.R. 1997. Response of Tifway 2 bermudagrass to fresh or composted broiler litter containing boric acid-treated paper bedding. Commun. Soil Sci. Plant Anal. 28:259-279.

Xu. Q., and B. Huang. 2001. Morphological and physiological characteristics associated with heat tolerance in creeping bentgrass. Crop Sci. 41:127-133.

E. A. Guertal *

Dep. of Agronomy and Soils, 253 Funchess Hall, Auburn Univ., AL 36849. Received 6 Feb. 2003. * Corresponding author (eguertal@acesag.auburn.edu).
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Title Annotation:Turfgrass Science
Author:Guertal, E.A.
Publication:Crop Science
Date:Jan 1, 2004
Words:4856
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