Page 7 - Transitioning Turfgrass
P. 7

th
                                                                           6  ETS Field Days
         01




          Site-Specific Management for the

          Reduction of Turfgrass Inputs



          Gerald Henry, PhD, Professor-Environmental Turfgrass Science, University of Georgia



          Turfgrass managers are often accused of exhib-  tion measurement.
          iting luxury consumption of several inputs such as   The  magnitude  and  frequency  of  spatial  varia-
          fertility, irrigation, cultivation etc. Recent research   tion with respect to several agronomic conditions
          has attempted to change this perception by en-  present  within  turfgrass  systems  requires  intense
          hancing sustainability through the development   sampling techniques for data acquisition. Research
          and implementation of efficient, site-specific turf-  was conducted to determine the minimal number
          grass management. The spatial variability of soil   of samples needed to accurately describe the spa-
          and plant parameters common to turfgrass envi-  tial variability of soil and plant parameters. Six
          ronments makes it very difficult to oversee entire   sampling  grid  sizes  (2.4  m  x  4.8  m,  4.8m  x  4.8
          areas under the same management plan (Fig. 1).   m, 4.8 m x 9.6 m, 9.6 m x 9.6 m, 9.6 m x 19.2 m,
          Therefore, the primary goal of site specific man-  and 19.2 m x 19.2 m) were employed for the spatial
          agement is to define boundaries of site specific   analysis of VWC, PR and NDVI when areas were
          management  units  (SSMUs)  (i.e.  management   near field capacity and under drier soil conditions.
          zones)  through  the  use  of  precision  agriculture
          concepts,  technologies,  and  products  (Photo
          1,  page  4).  Integrating  current  site  assessment
          equipment/sensors into daily management prac-     Cation Exchange Capacity
          tices will help turfgrass managers to apply inputs
          to areas where needed, when needed, and in the
          amount needed, resulting in management on a           meq 100 g-1
          smaller scale and reductions in overall inputs.         6,6-7,2
                                                                  7,3-7,7
                                                                  7,8-8,3
          Extensive research has been conducted at the            8,4-8,8  0 15 30  60 m
                                                                  8,9-9,4
          University of Georgia to determine optimal sam-         9,5-10
                                                                  11-11
          pling  technique,  timing,  and  application.  Re-
          search was conducted to compare handheld and          Organic Matter
          mobile  sensor  data  acquisition  of  soil  moisture
          [Volumetric  Water  Content  (VWC)],  soil  com-
          paction [Penetration Resistance (PR)], and turf-        %
          grass quality [Normalized Difference Vegetative         6,1-6,9
                                                                  7-7,6
                                                                  7,7-8,4
          Index (NDVI)]. Spatial maps of VWC and NDVI             8,5-9,1  0 15 30  60 m
                                                                  9,2-9,9
          displayed similar patterns of variability between       10-11
                                                                  12-11
          handheld and mobile devices, while spatial maps
          of PR were inconsistent due to device design and   Figure 1 Kriged maps of Cation Exchange Capacity
          user reliability. Consequently, mobile devices may   (CEC) and Organic Matter (OM) content of a fairway at
          provide the most reliable results for soil compac-  the Georgia Club Golf Course in Statham, GA in 2016.

                                                                                       3
   2   3   4   5   6   7   8   9   10   11   12