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Weed Control and Organic Mulches Affect Physiology and Growth of Landscape Shrubs

Authors:
Bert M. CreggMichigan State University, Department of Horticulture and Department of Forestry, A214 Plant and Soil Science, East Lansing, MI 48824

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Robert SchutzkiMichigan State University, Department of Horticulture, A218 Plant and Soil Science, East Lansing, MI 48820

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Abstract

Landscape mulches are widely promoted to improve soil moisture retention, suppress weeds, and improve the growth of landscape plants. The objective of this project was to determine the effect of common landscape mulches (pine bark, hardwood fines, cypress mulch, color-enhanced ground pallets) on soil moisture, soil pH, weed control, and physiology and growth of landscape shrubs. Two additional treatments were not mulched: no mulch + no weed control and no mulch + weed control. Growth was measured on eight taxa (Euonymus alatus ‘Compactus’, Spiraea ×bumalda ‘Goldflame’, Weigela florida ‘Java red’, Taxus ×media ‘Runyan’, Thuja occidentalis ‘Golden Globe’, Hydrangea paniculata ‘Tardiva’, Viburnum dentatum ‘Synnestvedt’, Viburnum trilobum ‘Compactum’). Leaf gas exchange [net photosynthesis and stomatal conductance (g s)] were measured on Hydrangea paniculata, V. dentatum, and V. trilobum only. All mulches increased soil moisture compared with no mulch + weed control. There was no difference in soil pH or foliar nitrogen among treatments. All mulches, except cypress mulch, increased plant growth of most shrub taxa compared with no mulch without weed control. Mulches increased g S relative to no mulch without weed control. Photosynthetic rates of plants mulched with cypress mulch were less than the other mulches and not different from no mulch. Overall, the result suggests that, except for cypress mulch, the organic mulches tested are equally effective in improving growth of landscape plants. Reduced photosynthetic efficiency and growth of shrubs with cypress mulch suggest potential allelopathic effects.

Landscape mulches are an important component to improving the sustainability of landscape systems. Mulches, particularly organic mulches, can enhance sustainability by reducing chemical inputs and the use of fossil fuels to maintain healthy and aesthetically pleasing landscapes. The effects of mulches on environmental factors and landscape plant growth have been widely studied [see Chalker-Scott (2007) for a comprehensive review]. Mulches provide an array of landscape benefits, including improving soil moisture (Fraedrich and Ham, 1982; Iles and Dosmann, 1999; Kraus, 1998; Litzow and Pellett 1993; Watson, 1988; Watson and Kupkowski, 1991), maintaining optimum soil temperatures (Fraedrich and Ham, 1982; Montague and Kjelgren, 2004), moderating energy budgets and reflected heat load (Montague et al., 2007), improving soil nutrition (Greenly and Rakow, 1995), and improving landscape plant growth (Green and Watson, 1989; Greenly and Rakow, 1995; Lithow and Pellett, 1993).

Although the overall benefits of mulches have been well established, a question we frequently field in our extension and outreach work with landscape professionals and homeowners is, “Which mulch should I use?” Distilling down the information on mulches can be difficult because many studies consider only one or two response factors or deal with mulches that may not be commonly available.

To gain greater insights into the effectiveness of mulches for midwestern landscapes, we established a landscape mulch study at the Michigan State University Horticulture Teaching and Research center in late Summer 2004. The goal of the project was to determine the response of several common landscape shrubs to four widely used and commercially available mulches (pine bark, cypress mulch, hardwood mulch, and color-enhanced ground recycled pallets) over 3 years. We chose to focus on organic mulches because their superiority over inorganic mulches has been well documented in the literature (Chalker-Scott, 2007). In addition to the mulches, we included two treatments without mulch, no mulch + no weed control and no mulch + weed control, to separate the effect of weed control from the overall mulch effect.

Specific objectives of the project were to determine the effect of mulch and weed control on shrub growth, photosynthetic gas exchange, foliar nutrition, soil moisture, soil pH, and populations of common weeds.

Materials and Methods

Site and treatments.

The study was installed in Aug. 2004 at the Michigan State University Teaching and Research Center near East Lansing, MI. The study area is flat and the soils are a Capac loam (fine-loamy, mixed, active, mesic Aquic Glossudalfs). The area had not been in crop production for the past 3 years and the existing vegetation was primarily perennial grasses that were mowed periodically. We prepared 24 3.7 m × 3.7-m (12-ft × 12-ft) plots by trenching around each plot to a depth of 0.9 m (3 ft) and lining the perimeter of the plots with heavy (6-mm thick) black plastic. Vegetation in the plots was sprayed with glyphosate and then rototilled ≈1 month before installation of the experiment. We planted 10 shrubs from eight taxa in each plot. Taxa used were burning bush (Euonymus alatus ‘Compactus’), ‘Goldflame’ spirea (Spiraea ×bumalda ‘Goldflame’), ‘Java red’ weigela (Weigela florida ‘Java red’), ‘Runyan’ yew (Taxus ×media ‘Runyan’), ‘Golden globe’ arborvitae (Thuja occidentalis ‘Golden Globe’), Tardiva hydrangea (Hydrangea paniculata ‘Tardiva’), Chicago Lustre® arrowwood viburnum (Viburnum dentatum ‘Synnestvedt’), and cranberrybush viburnum (Viburnum trilobum ‘Compactum’). One shrub of each taxa was planted in each plot except for ‘Golden Globe’ arborvitae and ‘Runyan’ yew, which were represented by two plants per plot as a result of greater availability. All plants were donated from a local wholesale nursery and grown in No. 3 (10.5-L) containers. Some plants exhibited circling roots, which were teased apart and separated by hand before planting. Root systems were not sliced or “butterflied.” After planting, we mulched plots to an uncompacted depth of 8 cm with one of four organic mulches: ground red pine bark, ground recycled pallets, hardwood bark fines, or ground cypress mulch (Table 1). Two additional plots in each replication were not mulched; one plot served as an unmulched control and the other was maintained weed-free by hand-weeding and directed sprays of glyphosate. The study was installed as a split plot in a randomized complete block with four blocks. Mulch was applied as the main plot factor and shrub taxa was considered the subplot factor. Blocks were arranged to account for potential variation in soil across the field. All plots were irrigated weekly in August and early Sept. 2004 to aid in initial plant establishment. Survival of all plants at the initiation of measurements in Spring 2005 was 100%. No fertilization was added during the study and no additional mulch was added after plot installation, i.e., plots were not “top-dressed.”

Table 1.

Description of weed control and mulch treatments in Michigan State University Landscape Mulch Trial.

Table 1.

Measurements.

We measured plant height (h) and crown width in two directions (w1 and w2 ) on each shrub at the beginning and end of the 2005, 2006, and 2007 growing seasons. Crown volume index (V) was calculated as V = h × w1 × w2 . Rainfall and reference evapotranspiation (ETo) for the site was compiled from the Michigan Automated Weather Network weather station located ≈600 m from the study. Reference evapotranspiration was estimated by the FAO Penment-Montheith calculation (Allen et al., 1998).

We measured soil moisture every 7 to 14 d on each plot through the 2005 and 2006 growing seasons using a portable TDR system (TRASE; Soil Moisture Equipment, Inc., Santa Barbara, CA). Soil moisture was measured at 0 to 15 cm and 0 to 45 cm below the soil surface near the center of each plot.

Photosynthetic gas exchange and stomatal conductance (g S) to water vapor were measured on Hydrangea paniculata, Viburnum dentatum, and Viburnum trilobum plants on two dates in 2006 and two dates in 2007 using a portable photosynthesis system (LI-6400; LI-COR, Inc., Lincoln, NE). Hydrangea and the two Viburnum species were selected for gas exchange measurements because they have relatively large leaves that completely covered the 2 × 3-cm leaf chamber of the portable photosynthesis system. This approach simplified gas exchange measurements and eliminated the need to correct gas exchange measurements resulting from partial coverage of the leaf chamber. All gas exchange measurements were completed near midday (1000 to 1600 hr) on clear days. To reduce environmental noise in the gas exchange data, the light control system on the LI-6400 was set to 1500 μmol·m−2·s−1, the temperature control block was set to the predicted high temperature for each measurement day, and the CO2 mixer was set to 400 ppm CO2. Three gas exchange measurement were collected on fully expanded leaves at the mid- to upper crown of each shrub. Measurements were logged when the real-time graphics display on the instrument indicated gas exchange was stable and the cv of the rolling average of photosynthesis calculated by the LI-6400 was less than 2%. Intrinsic water use efficiency (WUEi) was calculated from gas exchange measurements as: WUEi = A/gwv , where: A = net photosynthetic rate in μmol CO2/m−2·s−1 and gwv is leaf conductance to water vapor in mmol H2O/m−2·s−1.

In Aug. 2006, foliar nitrogen was determined for Hydrangea paniculata, Viburnum dentatum, and Viburnum trilobum. Approximately 20 g (fresh weight) of fully expanded leaves were collected from each plant. Leaves were oven-dried, ground, and analyzed at a commercial laboratory (Waters Agricultural Laboratory, Camilla, GA).

Soil pH was determined for each plot in Aug. 2006. Twelve soil samples were collected at a depth of 0 to 15 cm below the soil surface in each plot using a 17-mm diameter push-type soil probe and composited in a clean bucket. Soil samples were well mixed and a subsample was used for pH measurements. Soil pH was determined on each sample using a 1:1 (v:v) mix of soil and deionized water with a pH meter (Model AB15; Fisher Scientific, Pittsburgh, PA).

Weed competition was assessed near at the end of the 2006 growing season. A complete census of all weeds was conducted in each plot. Nine weeds were identified to species. Annual grasses were composited in one category. Additional weeds were counted as “other.”

Analysis.

Overall growth and survival data were analyzed by analysis of variance based on a split plot in a randomized complete block with mulch or weed control as the main plot and taxa as the subplot using the model yijk = μ + αi + βj + αβij + γk + αγik + ɛijk where: μ = the overall mean, αi = mulch/weed control, βj = block effect, αβij = main plot error term (Error A), γk = taxa effect, αγik = mulch/weed control × taxa interaction, ɛijk = subplot error (Error B).

Where significant (P < 0.05) mulch effects were indicated, weed population means were separated by Fisher's least significant difference test. All other means were separated by Tukey's Studentized range test.

Results

Weather.

Weather patterns varied among the 3 years of the study (Fig. 1). Year 2005 was the driest year during the study. Over the 2005 growing season, reference potential evapotranspiration exceeded rainfall by 341 mm. Reference ET exceeded rainfall in 18 of 23 weeks between 1 Apr. and 15 Sept. 2005. A late-season dry spell was noteworthy because only 19 mm of rain fell during a 7-week span from late July to mid-September. Rainfall was more consistent in 2006 than in 2005 and the rainfall deficit (–112 mm) was the smallest of the 3 study years. Year 2007 was intermediate between 2005 and 2006 in terms of total rainfall and rainfall deficit. A 7-week dry period occurred from early July until mid-Aug. 2007 during which only 31 mm of rain fell.

Fig. 1.
Fig. 1.

Weekly rainfall and reference evapotranspiration (ET) from Michigan Automated Weather Network Site at Michigan State University Horticulture Teaching and Research Center, East Lansing, MI, 2005 to 2007. Rainfall deficit = reference ET – rainfall.

Citation: HortScience horts 44, 5; 10.21273/HORTSCI.44.5.1419

Soil moisture.

Mulching increased (P < 0.05) soil moisture compared with no mulch + weed control at 0 to 15 cm and 0 to 45 cm in 2005 and 2006 (Table 2). There was no difference in soil moisture among mulches in either year at either depth. At 0- to 15-cm depth, soil moisture was slightly, but not significantly, lower in no mulch + weed control than without weed control. At 0 to 45 cm, soil moisture in the no weed control plot was greater than no mulch + weed control. Also, soil moisture increased without weed control in 2006 compared with 2005.

Table 2.

Mean (± se) volumetric soil moisture at 0- to 15-cm and 0- to 45-cm depth under mulches and without mulch, Michigan State University Mulch Study, 2005–2006.

Table 2.

Seasonal patterns of soil moisture without mulch + weed control and without weed control closely followed rainfall in 2005 (Fig. 2). Soil moisture peaked after heavy rainfall in late June and late July and then declined. Soil moisture reached the lowest levels during the dry-down period in August and early Sept. 2005. In 2006, rainfall was more consistent than in 2005 and soil moisture was generally higher and treatment effects were less pronounced at the 0- to 15-cm depth. For the entire study, there were no differences in soil moisture among any of the mulches on any of the 27 measurements dates at either 0- to 15-cm or 0- to 45-cm soil depth.

Fig. 2.
Fig. 2.

Mean (± se) volumetric soil moisture at 0 to 15 cm and 0 to 45 cm for landscape plots with 8 cm organic mulches or unmulched with and without weed control, Michigan State University Horticulture Teaching and Research, East Lansing, MI, 2005 to 2006. N = 4 for all means.

Citation: HortScience horts 44, 5; 10.21273/HORTSCI.44.5.1419

Soil pH.

Soil pH did not vary (P > 0.05) among the treatments (data not shown). Mean pH of all treatments ranged from neutral to slightly acidic.

Weed control.

Mulches were effective in reducing many of the most common weeds in the study area (Table 3). Populations of common dandelion, annual grasses, redroot pigweed, and horseweed were lower (P < 0.05) on mulched plots than plots with no weed control. Populations of annual sowthistle, however, were greater (P < 0.05) on plots mulched with cypress, ground pallets, or hardwood fines than the no weed control plots. This suggests that the mulch itself may have provided an adequate seedbed for germination and development of sowthistle or that the mulch depth was insufficient to provide adequate control (Abouziena et al., 2008).

Table 3.

Mean weed counts in plots with organic mulches or unmulched with and without weed control, Michigan State University Horticulture Teaching and Research, East Lansing, MI, Sept. 2006.

Table 3.

Growth.

Treatment, taxa, and the interaction of treatment × taxa affected (P < 0.01) crown height, crown diameter, and crown volume of shrubs after 3 years (Table 4). Patterns of variation were similar among growth variables; therefore, only height growth is presented in detail to simplify data presentation (Fig. 3). Plants mulched with pine bark, hardwood fines, or ground pallets grew more than plants in the unmulched plots without weed control for five of eight taxa. For all taxa, there was no difference in growth of plants mulched with pine bark, hard wood fines, or ground pallets. Weed control alone increased plant growth compared with plants in the no weed control plots, although the difference was significant only for V. trilobum. Averaged across all taxa, plants mulched with cypress mulch grew less (P < 0.01) than plants mulched with the other organic materials (data not shown). Growth of shrubs mulched with cypress mulch did not differ (P > 0.25) from growth of plants in the no mulch + weed control plots for any of the taxa.

Table 4.

Summary analysis of variance (F-values) for 3-year growth response of landscape shrubs grown with organic mulches or unmulched with and without weed control, Michigan State University Horticulture Teaching and Research, East Lansing, MI.

Table 4.
Fig. 3.
Fig. 3.

Mean (± se) cumulative 3-year height growth of landscape shrubs mulched with four types of organic mulch or unmulched with and without weed control. Means within a species denoted by the same letter are not different at the P = 0.05 level based on Tukey's Studentized range test.

Citation: HortScience horts 44, 5; 10.21273/HORTSCI.44.5.1419

Viburnum trilobum plants grew more than plants from the other taxa, averaging 0.87 m in height growth, followed by Hydrangea paniculata at 0.62 m. Euonymus plants grew slowly and several plants suffered dieback, particularly with no mulch/no weed control or mulched with recycled pallets.

Foliar nitrogen.

Treatment and taxa affected (P < 0.05) foliar nitrogen (N) concentration, but the interaction effect of taxa × treatment was not significant. Plants mulched with hardwood fines had greater foliar N concentration than plants with no weed control or plants mulched with cypress mulch (Table 5). There was no difference in foliar N among the other mulch treatments. Among the taxa, Hydrangea plants had greater (P < 0.05) foliar N than Viburnum plants.

Table 5.

Mean foliar nitrogen (N) concentration of Hydrangea paniculata ‘Tardiva’, Viburnum dentatum ‘Synnestvedt’, and Viburnum trilobum ‘Bailey Compact’ grown for 2 years with organic mulches or unmulched with and without weed control, Michigan State University Horticulture Teaching and Research, East Lansing, MI.

Table 5.

Photosynthetic gas exchange.

All mulches, except cypress mulch, increased (P < 0.05) net photosynthesis compared with no weed control (Table 6) and similar patterns were observed within specific taxa investigated (Fig. 4). Net photosynthesis of plants without mulch + weed control or cypress mulch was intermediate between no weed control and the other mulches. Mulches generally increased g S to water vapor, reflecting the improvement of soil moisture availability with all of the mulches. Lower photosynthesis of plants with cypress mulch relative to the other mulches appears to be related to nonstomatal or biochemical changes in the photosynthetic system. G S (gwv ) was affected by the presence of mulch, but there was no difference in gwv among mulches (Table 6). Intrinsic water use efficiency (ratio of A/gwv ) decreased significantly for plants mulched with cypress compared with no mulch + weed control.

Table 6.

Mean net photosynthesis, stomatal conductance (g S) to water vapor, and intrinsic water use efficiency of landscape shrubs growth with organic mulches or unmulched with and without weed control, Michigan State University Horticulture Teaching and Research, East Lansing, MI, 2006 to 2007.

Table 6.
Fig. 4.
Fig. 4.

Mean (± se) net photosynthesis of Hydrangea paniculata ‘Tardiva’, Viburnum dentatum ‘Synnestvedt’, and Viburnum trilobum ‘Compactum’ grown with organic mulches or unmulched with and without weed control, Michigan State University Horticulture Teaching and Research, East Lansing, MI. Means averaged from four dates in 2006 to 2007. Means within a species denoted by the same letter are not different at the P = 0.05 level based on Tukey's Studentized range test.

Citation: HortScience horts 44, 5; 10.21273/HORTSCI.44.5.1419

Discussion

The results of this study support the preponderance of data in the literature, which show that organic mulches improve growth of landscape plants by controlling weeds and conserving soil moisture. There were, however, several key observations that departed from commonly observed trends or perceptions regarding the effects of mulch on the landscape environment and growth of landscape plants. Subsequently, we discuss some of these key observations.

Improved soil moisture on no weed control plots compared with no mulch + weed control.

Our a priori hypothesis was that, among all treatments, soil moisture would be lowest without weed control and next lowest on no mulch + weed control plots based on the assumption that total evapotranspiration from soil would be greater with weeds than without. Counter to our hypothesis, soil moisture was greater without weed control than with weed control. We speculate that the increase in soil moisture without weed control is the result of several factors. First, weed populations were dense enough by Summer 2005 to shade a large portion of the soil surface, presumably reducing soil temperature and subsequent evaporation. Second, as annual weeds died, they effectively formed a mulch layer, which functioned similar to the organic mulches, at least in terms of soil moisture retention. Third, landscape shrubs without mulch + weed control generally grew more than shrubs without mulch. Larger crowns on the shrubs with weed control may have contributed to greater overall transpiration and soil moisture depletion, particular at the 0- to 45-cm soil depth, than shrubs without weed control.

Lack of mulch effects on soil pH and foliar plant nutrition.

Chalker-Scott (2007) noted that two assumptions regarding organic mulches; acidification of soil and nutrient “tie-up” are rarely supported by the literature. In the present study, there was no difference in soil pH among any of the mulches or between mulched and unmulched plots. Similarly, Greenly and Rakow (1995) observed no difference in soil pH of soils mulched for 2 years with 0, 7.5, 15, or 25 cm of shredded hardwood chips or chipped pine bark. Iles and Dosmann (1999) found that pine mulch and hardwood mulch increased soil pH compared with bare ground. In the present study, we found no evidence of nutrient depletion or reduced foliar N of plants grown with mulch compared with bare ground (no mulch + weed control). Within the mulch treatments, plants grown with hardwood mulch had greater foliar N than plants grown with cypress mulch. The hardwood material was ground finer than the other mulches, which may lead to more rapid decomposition, especially relative to cypress, which contains a large amount of extractives (Panshin and deZeeuw, 1980). Our results are consistent with several mulch studies in the arboricultural literature, which suggest that organic mulches have no effect, or may improve, nutrient availability (Fraedrich and Ham, 1982; Greenly and Rakow, 1995).

Reduction in growth and photosynthetic efficiency of plants mulched with cypress mulch compared with other mulches.

Among the mulches we observed, a general trend that landscape shrubs grew less with cypress mulch than with the other mulches, particularly pine bark or hardwood mulch. Circumstantial evidence suggests that the effect of cypress mulch may, at least in part, be allelopathic. Allelopathic effects of mulch are generally viewed in terms of suppression of seed germination, especially weed seeds. For example, Duryea et al. (1999) observed allelopathic effects of several fresh mulches in bioassays on germination of lettuce seeds. Salicylic acid from bark of Chamaecyparis obtusa induced allelopathic effects on seeds of plants native to the species’ range in Taiwan as well as on seeds of exotic plants (Tseng et al., 2007). Allelopathic effects on newly planted or existing woody landscape plants, however, have not been documented.

Conclusively demonstrating allelopathic effects can often be extraordinarily difficult (Halsey, 2004), but several lines of evidence suggest it may occur with cypress mulch. As noted previously, soil pH and foliar nutrient levels were similar among mulches tested, indicating neither factor can explain reduced growth of plants with cypress mulch. Soil moisture and plant moisture stress (as evidenced by g S to water vapor) were nearly identical among mulches, indicating all mulches tested were equally effective in reducing plant stress. However, net photosynthetic rate of plants grown with cypress mulch was the lowest among mulches tested and WUE (the ratio of net photosynthesis to g S) of plants with cypress mulch was lowest among all treatments applied. It should be noted that the plants studied were newly planted at the start of the study. It is uncertain whether mulching well-established plants with cypress would have similar impacts. Clearly, additional factors may be responsible for the reduced shrub growth observed with cypress mulch, but the potential role of allelopathy warrants further investigation.

Literature Cited

  • Abouziena, H.F. , Hafez, O.M. , El-Metwally, I.M. , Sharma, S.D. & Singh, M. 2008 Comparison of weed suppression and mandarin fruit yield and quality obtained with organic mulches, synthetic mulches, cultivation, and glyphosate HortScience 43 795 799

    • Search Google Scholar
    • Export Citation
  • Allen, R.G. , Pereira, L.S. , Raes, D. & Smith, M. 1998 Crop evapotranspiration—Guidelines for computing crop water requirements. FAO Irrigation and Drainage Paper 56 Food and Agriculture Organization of the United Nations Rome, Italy

    • Search Google Scholar
    • Export Citation
  • Chalker-Scott, L. 2007 Impact of mulches on landscape plants and the environment—A review J. Environ. Hort. 25 239 249

  • Duryea, M.L. , English, R.J. & Hermansen, L.A. 1999 A comparison of landscape mulches: Chemical, allelopathic, and decomposition properties J. Arbor. 25 88 97

    • Search Google Scholar
    • Export Citation
  • Fraedrich, S.W. & Ham, D.L. 1982 Wood chip mulching around maples: Effect on tree growth and soil characteristics J. Arbor. 8 85 89

  • Green, T.L. & Watson, G.W. 1989 Effects of turfgrass and mulch on establishment and growth of bareroot sugar maples J. Arbor. 15 268 272

    • Search Google Scholar
    • Export Citation
  • Greenly, K. & Rakow, D. 1995 The effects of mulch type and depth of weed and tree growth J. Arbor. 21 225 232

  • Halsey, R.W. 2004 In search of allelopathy: An eco-historical view of the investigation of chemical inhibition in California coastal sage scrub and chamise J. Torrey Bot. Soc. 131 343 367

    • Search Google Scholar
    • Export Citation
  • Iles, J.K. & Dosmann, M.S. 1999 Effect of organic and mineral mulches on soil properties and growth of ‘Fairview Flame R’ red maples trees J. Arbor. 25 163 167

    • Search Google Scholar
    • Export Citation
  • Kraus, H.T. 1998 Effects of mulch on soil moisture and growth of desert willow HortTechnology 8 588 590

  • Litzow, M. & Pellett, H. 1993 Influence of mulch materials on growth of green ash J. Arbor. 9 7 11

  • Montague, T. & Kjelgren, R. 2004 Energy balance of six common landscape surfaces and the influence of surface properties on gas exchange of four containerized tree species Scientia Hort. 100 229 249

    • Search Google Scholar
    • Export Citation
  • Montague, T. , McKenney, C. , Maurer, M. & Winn, B. 2007 Influence of irrigation volume and mulch on establishment of select shrub species Arboriculture and Urban Forestry 33 202 209

    • Search Google Scholar
    • Export Citation
  • Panshin, A.J. & deZeeuw, C 1980 Textbook of wood technology 4th Ed McGraw-Hill New York, NY

  • Tseng, M. , Wen-Rong, L. , Hsieh, C. & Kuo, Y. 2007 Allelopathy on bark of downed logs of Chamaecyparis obtusa sieb. and Zucc. var. formosana (Hayata) Rehder J. Chem. Ecol. 33 1283 1296

    • Search Google Scholar
    • Export Citation
  • Watson, G.W. 1988 Organic mulch and grass competition influence tree root development J. Arbor. 14 200 203

  • Watson, G.W. & Kupkowski, G. 1991 Effects of a deep layer of mulch on the soil environment and tree root growth J. Arbor. 17 242 245

  • View in gallery

    Weekly rainfall and reference evapotranspiration (ET) from Michigan Automated Weather Network Site at Michigan State University Horticulture Teaching and Research Center, East Lansing, MI, 2005 to 2007. Rainfall deficit = reference ET – rainfall.

  • View in gallery

    Mean (± se) volumetric soil moisture at 0 to 15 cm and 0 to 45 cm for landscape plots with 8 cm organic mulches or unmulched with and without weed control, Michigan State University Horticulture Teaching and Research, East Lansing, MI, 2005 to 2006. N = 4 for all means.

  • View in gallery

    Mean (± se) cumulative 3-year height growth of landscape shrubs mulched with four types of organic mulch or unmulched with and without weed control. Means within a species denoted by the same letter are not different at the P = 0.05 level based on Tukey's Studentized range test.

  • View in gallery

    Mean (± se) net photosynthesis of Hydrangea paniculata ‘Tardiva’, Viburnum dentatum ‘Synnestvedt’, and Viburnum trilobum ‘Compactum’ grown with organic mulches or unmulched with and without weed control, Michigan State University Horticulture Teaching and Research, East Lansing, MI. Means averaged from four dates in 2006 to 2007. Means within a species denoted by the same letter are not different at the P = 0.05 level based on Tukey's Studentized range test.

  • Abouziena, H.F. , Hafez, O.M. , El-Metwally, I.M. , Sharma, S.D. & Singh, M. 2008 Comparison of weed suppression and mandarin fruit yield and quality obtained with organic mulches, synthetic mulches, cultivation, and glyphosate HortScience 43 795 799

    • Search Google Scholar
    • Export Citation
  • Allen, R.G. , Pereira, L.S. , Raes, D. & Smith, M. 1998 Crop evapotranspiration—Guidelines for computing crop water requirements. FAO Irrigation and Drainage Paper 56 Food and Agriculture Organization of the United Nations Rome, Italy

    • Search Google Scholar
    • Export Citation
  • Chalker-Scott, L. 2007 Impact of mulches on landscape plants and the environment—A review J. Environ. Hort. 25 239 249

  • Duryea, M.L. , English, R.J. & Hermansen, L.A. 1999 A comparison of landscape mulches: Chemical, allelopathic, and decomposition properties J. Arbor. 25 88 97

    • Search Google Scholar
    • Export Citation
  • Fraedrich, S.W. & Ham, D.L. 1982 Wood chip mulching around maples: Effect on tree growth and soil characteristics J. Arbor. 8 85 89

  • Green, T.L. & Watson, G.W. 1989 Effects of turfgrass and mulch on establishment and growth of bareroot sugar maples J. Arbor. 15 268 272

    • Search Google Scholar
    • Export Citation
  • Greenly, K. & Rakow, D. 1995 The effects of mulch type and depth of weed and tree growth J. Arbor. 21 225 232

  • Halsey, R.W. 2004 In search of allelopathy: An eco-historical view of the investigation of chemical inhibition in California coastal sage scrub and chamise J. Torrey Bot. Soc. 131 343 367

    • Search Google Scholar
    • Export Citation
  • Iles, J.K. & Dosmann, M.S. 1999 Effect of organic and mineral mulches on soil properties and growth of ‘Fairview Flame R’ red maples trees J. Arbor. 25 163 167

    • Search Google Scholar
    • Export Citation
  • Kraus, H.T. 1998 Effects of mulch on soil moisture and growth of desert willow HortTechnology 8 588 590

  • Litzow, M. & Pellett, H. 1993 Influence of mulch materials on growth of green ash J. Arbor. 9 7 11

  • Montague, T. & Kjelgren, R. 2004 Energy balance of six common landscape surfaces and the influence of surface properties on gas exchange of four containerized tree species Scientia Hort. 100 229 249

    • Search Google Scholar
    • Export Citation
  • Montague, T. , McKenney, C. , Maurer, M. & Winn, B. 2007 Influence of irrigation volume and mulch on establishment of select shrub species Arboriculture and Urban Forestry 33 202 209

    • Search Google Scholar
    • Export Citation
  • Panshin, A.J. & deZeeuw, C 1980 Textbook of wood technology 4th Ed McGraw-Hill New York, NY

  • Tseng, M. , Wen-Rong, L. , Hsieh, C. & Kuo, Y. 2007 Allelopathy on bark of downed logs of Chamaecyparis obtusa sieb. and Zucc. var. formosana (Hayata) Rehder J. Chem. Ecol. 33 1283 1296

    • Search Google Scholar
    • Export Citation
  • Watson, G.W. 1988 Organic mulch and grass competition influence tree root development J. Arbor. 14 200 203

  • Watson, G.W. & Kupkowski, G. 1991 Effects of a deep layer of mulch on the soil environment and tree root growth J. Arbor. 17 242 245

Bert M. CreggMichigan State University, Department of Horticulture and Department of Forestry, A214 Plant and Soil Science, East Lansing, MI 48824

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Robert SchutzkiMichigan State University, Department of Horticulture, A218 Plant and Soil Science, East Lansing, MI 48820

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Contributor Notes

We thank Dr. Dan Brainard, Dr. Brad Rowe, and three anonymous reviewers for their helpful reviews of this manuscript. We gratefully acknowledge Dr. Gerry Adams for initial planning and development of the project and Dan Little for assessing weed populations. We thank Anna Arend, Darren Gladstone, Jennifer Hunnell, Sara Tanis, and Wendy Klooster for assisting with field data collection.

Associate Professor.

To whom reprint requests should be addressed; e-mail cregg@msu.edu.

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