soil compaction at bonnaroo music and arts festival ...€¦ · soil compaction at bonnaroo music...

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Soil Compaction at Bonnaroo Music and Arts Festival, Manchester, TN St. Thomas LeDoux, University of Tennessee, Knoxville, Department of Earth and Planetary Sciences Hakansson, I., W.B. Voorhees, and H. Riley. 1988. Vehicle and wheel factors influencing soil compaction and crop response in different traffic regimes. Soil and Tillage Research , 11(3-4), 239–282. Horrigan, L., R.S. Lawrence, and P. Walker. 2002. How sustainable agriculture can address the environmental and human health harms of industrial agriculture. Environmental Health Perspectives, 110(5), 445-456. REFERENCES The results of the comprehensive model suggest that: Across all treatment areas, compaction increased as a result of the event. Maximum depth of penetration varies by location and soil area- density. Soil area-density also varies by location. There was no change in the control. Other considerations: The relationships demonstrated by the first model are highly variable from stage-to-stage. Analyses of depth of penetration by sample period for individual stages would be best supplemented by increasing sample size. Analyses of spatial variability in soil area-density would be best supplemented by gathering soil profiles of each stage area. The control model would be best supplemented by additional sample plots nearer each stage. Limitations: Event had taken place on the same land for 10 years prior to sampling. Late arrival to the event. Limited access to some stage areas. Confounded results due to yearly sodding of some stage areas. No data for soil moisture content. No data related to runoff of erosion. Bonnaroo is massive. CONCLUSIONS Drs. Michael McKinney, Devon Burr, and James Fordyce. AC Entertainment, Inc. Superfly Productions, Inc. Clean Vibes, LLC. Jessica Welch. ACKNOWLEDGEMENTS RESULTS Figure 1: Comprehensive distribution of the data ( depth of penetration) by sample period (June 6, 2012 vs. June 15, 2012) for both treatments (areas 1-6) and control (area 7). Areas 1-6 demonstrated a significant effect on depth of penetraton by all individual factors – location (F 5,504 = 19.1624, P < 0.0001), soil area- density ( F 2,504 = 344.8898, P < 0.0001), and sample period (F 1,504 = 21.8651, P < 0.0001) – as well as a significant interaction between location and soil area-density (F 10,504 = 4.0461, P < 0.0001). The control model demonstrated a significant effect by soil area-density on depth of penetration (F 2,89 = 54.4234, P < 0.0001), but no effect by sample period (F 1,89 = 0.2413, P < 0.6245). Figure 2: Distribution of the data ( depth of penetration) by sample period and location. For each sample area, soil area-density had a significant effect on depth of penetration (for all areas, P < 0.001), but only two sample areas, What (inner) and This, detected a significant interaction (at α = 0.05) between depth of penetration and sample period. MATERIALS & METHODS Samples taken using a hand-penetrometer. 270 samples taken before and after the festival among seven areas (6 stages, 1 control) measuring maximum depth of penetration at area-density thresholds of 70, 140, and 210 kg/m 2 Model 1: Variation in depth of penetration by soil area-density, location and sample period was examined using a full-factorial ordinary least squares model (ANOVA). Model 2: Variation in depth of penetration by soil area-density and sample period was examined individually for each location using a two-factor ANOVA. Model 3: Variation in depth of penetration by sample period was examined individually for soil area-density threshold using a single-factor ANOVA. Figure 3: Distribution of the data (depth of penetration) by sample period and soil area-density. This model showed that while significant changes in depth of penetration occurred at thresholds of 70 kg/m 2 (F 1,179 = 4.5291, P = 0.0348) and 140 kg/m 2 ( F 1,179 = 16.3243, P < 0.0001), only a marginally significant change occurred at the most critical threshold, 210 kg/m 2 (F 1,179 = 3.3855, P = 0.0675). While the general trend in depth of penetration at 210 kg/m 2 still decreased, the overall impact is considerably less in a single year than at lower soil area densities. This study aims to determine whether detrimental soil compaction occurred at an outdoor music festival hosting approximately 80,000 patrons. Excessive compaction by heavy machinery and foot traffic has the potential to reduce soil moisture and fertility, decrease vegetation, and ultimately increase erosion within event grounds (Hakansson et al. 1988; Horrigan et al. 2002). BACKGROUND

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Page 1: Soil Compaction at Bonnaroo Music and Arts Festival ...€¦ · Soil Compaction at Bonnaroo Music and Arts Festival, Manchester, TN St. Thomas LeDoux, University of Tennessee, Knoxville,

Soil Compaction at Bonnaroo Music and Arts Festival, Manchester, TNSt. Thomas LeDoux, University of Tennessee, Knoxville, Department of Earth and Planetary Sciences

•Hakansson, I., W.B. Voorhees, and H. Riley. 1988. Vehicle and wheel factors influencing soil compaction and crop response in different traffic regimes. Soil and Tillage Research, 11(3-4), 239–282.

•Horrigan, L., R.S. Lawrence, and P. Walker. 2002. How sustainable agriculture can address the environmental and human health harms of industrial agriculture. Environmental Health Perspectives, 110(5), 445-456.

REFERENCES

The results of the comprehensive model suggest that: •Across all treatment areas, compaction increased as a result of theevent.

•Maximum depth of penetration varies by location and soil area-density.

•Soil area-density also varies by location.•There was no change in the control.

Other considerations:•The relationships demonstrated by the first model are highly variablefrom stage-to-stage.

•Analyses of depth of penetration by sample period for individualstages would be best supplemented by increasing sample size.

•Analyses of spatial variability in soil area-density would be bestsupplemented by gathering soil profiles of each stage area.

•The control model would be best supplemented by additional sampleplots nearer each stage.

Limitations:•Event had taken place on the same land for 10 years prior tosampling.

•Late arrival to the event.•Limited access to some stage areas.•Confounded results due to yearly sodding of some stage areas.•No data for soil moisture content.•No data related to runoff of erosion.•Bonnaroo is massive.

CONCLUSIONS

•Drs. Michael McKinney, Devon Burr, and James Fordyce.•AC Entertainment, Inc.•Superfly Productions, Inc.•Clean Vibes, LLC.•Jessica Welch.

ACKNOWLEDGEMENTS

RESULTSFigure 1:

Comprehensive distribution of the data (depth ofpenetration) by sample period (June 6, 2012 vs.June 15, 2012) for both treatments (areas 1-6) andcontrol (area 7).

Areas 1-6 demonstrated a significant effect ondepth of penetraton by all individual factors –location (F5,504 = 19.1624, P < 0.0001), soil area-density ( F2,504 = 344.8898, P < 0.0001), and sampleperiod (F1,504 = 21.8651, P < 0.0001) – as well as asignificant interaction between location and soilarea-density (F10,504 = 4.0461, P < 0.0001). The control model demonstrated a significanteffect by soil area-density on depth of penetration(F2,89 = 54.4234, P < 0.0001), but no effect bysample period (F1,89 = 0.2413, P < 0.6245).

Figure 2:

Distribution of the data (depth of penetration) by sample period and location.

For each sample area, soil area-density had a significant effect on depth of penetration (for all areas,P < 0.001), but only two sample areas, What (inner) and This, detected a significant interaction (at α =0.05) between depth of penetration and sample period.

MATERIALS & METHODS

Samples taken using a hand-penetrometer.

•270 samples taken•before and after the festival•among seven areas (6 stages, 1 control)

•measuring maximum depth of penetration •at area-density thresholds of 70, 140, and210 kg/m2

Model 1: Variation in depth of penetration bysoil area-density, location and sample periodwas examined using a full-factorial ordinaryleast squares model (ANOVA).

Model 2: Variation in depth of penetration bysoil area-density and sample period wasexamined individually for each location using atwo-factor ANOVA.

Model 3: Variation in depth of penetration bysample period was examined individually forsoil area-density threshold using a single-factorANOVA.

Figure 3:Distribution of the data (depth of penetration) bysample period and soil area-density.

This model showed that while significant changesin depth of penetration occurred at thresholds of70 kg/m2 (F1,179 = 4.5291, P = 0.0348) and 140 kg/m2

( F1,179 = 16.3243, P < 0.0001), only a marginallysignificant change occurred at the most criticalthreshold, 210 kg/m2 (F1,179 = 3.3855, P = 0.0675).

While the general trend in depth of penetration at210 kg/m2 still decreased, the overall impact isconsiderably less in a single year than at lowersoil area densities.

This study aims to determine whetherdetrimental soil compaction occurred at anoutdoor music festival hosting approximately80,000 patrons.

Excessive compaction by heavy machineryand foot traffic has the potential to reduce soilmoisture and fertility, decrease vegetation, andultimately increase erosion within eventgrounds (Hakansson et al. 1988; Horrigan etal. 2002).

BACKGROUND