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| November 2006 |
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Testing, testing, testing Vigilant testing during root-zone mix production is a key step in putting green construction.
Editor’s note: The USGA updated its putting green construction recommendations in 2004. The data in this report meet both the recommendations that were in effect in 2003 and the current Laboratory testing plays two very important roles whenever new greens are constructed or existing greens are renovated. The first role is to provide an initial evaluation of the root-zone materials proposed for the project to determine whether they meet the project specifications. Using materials that meet project specifications helps to ensure the greens will perform as desired. The second role of testing is to monitor quality control. Quality-control testing should be performed throughout the production of the root-zone materials to ensure the use of consistent materials throughout the golf course. When should testing be performed? The quality-control testing program begins at the start of the mix preparation. The root-zone blender (usually a company specializing in blending root-zone mixes for golf courses or a specialist at the sand plant) will be attempting to calibrate its equipment. Initial calibration samples are sent to the lab to determine when a mix has been prepared that meets project specifications and/or the wishes of the superintendent. Once an acceptable material has been prepared, the testing data for this mix is used as a benchmark for future quality-control samples. The ongoing production samples are then compared to the benchmark results, and they are rejected or approved based on their consistency. Quality-control testing is usually performed at a rate of one sample for every 1,000 tons of root-zone mix. This equates to five to 10 quality-control samples for an 18-hole golf course. Other testing frequencies may be used depending on project requirements or concerns about the materials being used. Frequency of quality-control sampling is very important for ensuring consistent material throughout a construction site. A good rule of thumb for determining sampling frequency for greens and sports fields is the following formula: (Number of inches of material) × 84 = Tons of material per QC sample Therefore, for a 12-inch root-zone, one quality-control sample should be taken for every 1,000 tons of material. Sampling
Stockpiled materials are tested before shipment to the project site to ensure they meet project specifications. The superintendent or the owner’s representative should perform the sampling or at least be present whenever construction materials are sampled. An accurate representative sample is critical to getting valid testing results, and the ability to extrapolate the laboratory results to the field depends on how accurately the sample represents the bulk material. As described by the USGA Green Section, the process of obtaining an accurate sample is fairly simple. A PVC pipe about 45 to 50 inches long, cut at a 45-degree angle at one end, is used as a sample collection tube. A rubber mallet is useful for tapping samples out of the pipe. At least eight sampling locations should be randomly selected for a 1,000-ton stockpile. Samples should be taken from the top to the bottom and around the circumference of the pile. To take a sample, brush away the outer 6 inches of the pile and push the clean pipe as far as possible into the stockpile. Pull the pipe out and tap the sample into a clean bucket. Thoroughly mix the material after all the samples are taken. Remove one gallon of material from the bucket to fill a zip-lock bag. Label the sample with a permanent marker, indicating from which stockpile the sample was taken. To protect the samples during shipment, it’s usually best to send the samples double bagged in a sturdy box with sufficient packing material included. Sample identifications should always be on the outside of the sample bag or container. A letter or testing request form should also be included with the sample submittal. The letter should include any pertinent sampling information, testing required, information on how to contact you and where to send the report. Testing
The initial evaluation phase involves prequalification of the root-zone materials. Sand obtained from local sources is sent in to the lab for gradation testing according to USGA procedures. Once acceptable materials are found, the chosen root-zone sand and amendment are mixed in the lab (usually in two different ratios). An experienced lab should have the knowledge to prepare test mixes that will meet the project specifications based on the sand particle size and amendment characteristics. USGA physical evaluation tests are then performed on the mixes. Physical evaluation testing includes infiltration rate (saturated hydraulic conductivity), particle density, bulk density, porosities, organic matter content (if applicable) and pH. After the testing is completed, a report comparing the results to the USGA recommendations and/or project specifications is then prepared. This report should be distributed to all interested parties (superintendent, architect, builder and blender). These results are evaluated to determine which mix ratio best meets the project needs. The second stage of testing is the field calibration phase, which sets the baseline for the mix that is being prepared in the field and delivered to the golf course. For calibration, 200 tons of root-zone mix is prepared and sampled, and the sample is sent to the lab for testing. Particle size, organic matter and performance evaluation tests are performed to verify that the mix meets USGA recommendations or project specifications. If the results for the calibration sample are approved, they are used to establish the target values for the quality-control program. If they are not approved, the blender needs to recalibrate and send another sample. Quality-control testing is the final testing phase. Quality-control testing can include the complete series of tests performed in stages one and two, or only tests for particle size and organic matter. The results of the quality-control samples are compared to the calibration sample results. If the results for a stockpile are consistent with the target values, then that stockpile is considered acceptable, and it can be delivered to the site. If a quality-control sample is not consistent, then the entire stockpile may be rejected. Evaluating the data
In 2003, the Village Links of Glen Ellyn (Ill.) embarked on a complete renovation of its 18-hole course. This public facility, which had hosted the Western Open qualifying since 1980, was going to rebuild its greens to meet USGA recommendations. The facility’s veteran staff included head superintendent and 26-year GCSAA member Tim Kelly (Class A) and assistants Dave Buckley and Chris Pekarek. As the project progressed, Buckley was designated to obtain sand from local suppliers and submit them for testing. Particle size results indicated that the submitted sand met USGA recommendations and project requirements. Then two laboratory mixes were prepared from the sand and peat preferred by the golf course and the construction contractor. From these lab mixes, a desirable sand-to-peat ratio was determined. The particle size and performance test results for the first 100-ton sample met the USGA recommendations for putting green construction. The results for these samples were also acceptable to the parties involved in the construction at the Village Links of Glen Ellyn. The first 100-ton sample was thus used as the baseline sample for the quality-control program. Tolerances (also known as acceptance limits) were calculated based on confidence intervals developed by the USGA to aid in determining the consistency of the prepared root-zone mix. The calculated tolerances indicate guidelines for evaluating acceptable deviations from the calibration sample. Throughout the remainder of the root-zone blending for the Village Links project, Buckley obtained samples as the 1,000-ton stockpiles were prepared. Samples were then sent to the lab for testing and comparison to the acceptance limits. As can be seen in Table 1, the gravel and/or fine sand fractions were outside of tolerance for some of the quality-control samples. Table 2 also shows some of the porosities outside of limits. Since these results are outside of the tolerances, the results were further evaluated to determine whether the mix was acceptable or should be rejected. It was decided that the mixes were still acceptable. The gradation deviations were very small, and the overall data set was quite consistent. The porosity differences were also considered small, and no significant difference in performance was expected from the various stockpiles. Once the testing results were approved, then the stockpile material was shipped to the golf course. Buckley advises visually examining the material that is actually delivered to the site to check for potential contamination during loading and/or shipping.
The decision to accept or refuse a stockpile mix that is outside of tolerances is critical to the golf course and to the suppliers. Acceptance of an inconsistent or improper mix can result in having greens that are inconsistent and difficult to properly maintain. Rejecting a greens mix that should have been accepted can result in increased cost to the project or to the vendors. All available data, as well as any field observations that can be made, should be evaluated when making decisions regarding results that are slightly outside of tolerances. Conclusion The root-zone testing program performed for the Village Links of Glen Ellyn demonstrates that diligent sampling and testing provides assurance that the mix will meet the project’s needs. Two years after construction, the staff is pleased with the performance of their new greens. Others must be noticing, too, because in summer 2005, the golf course held U.S. Open qualifying in addition to its normal schedule.
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