Appendix A. Tables showing additional details on plant and soil characteristics and responses.
TABLE A1. Soil variables measured in field observational plots.
| Variable | Analytical method | Range of values (mean ± SE) |
| Soil moisture | Gravimetric | 17.3–52.6 % by w (33.0 ± 1.4) |
| pH | Orion Microprocessor pH/millivolt Meter Model 811 | 4.9–5.8 (5.4 ± 0.04) |
| Ammonium | Flow Injection Analysis Colorimetry by QuikChem Method 10-107-06-2-A | 0.2–3.2 Corrected mg N/L (1.2 ± 0.1) |
| Nitrate | Flow Injection Analysis Colorimetry by QuikChem Method 10-107-04-1-A | 0.06–2.1 Corrected mg N/L (0.5 ± 0.08) |
| Total organic carbon | High Temperature Catalytic Combustion | 10.2–40.4 mg C/L (21.2 ± 1.0) |
| Total nitrogen | Chemiluminescence Detection and Combustion | 1.4–5.6 mg N/L (3.1 ± 0.2) |
| Total phosphorous | Colorimetry | 554.55–1887.32 mg P/kg soil (1044.6 ± 130.6) |
TABLE A2. Species of grasses used in the greenhouse fertilization experiment. Seed for the experimental grass species was hand collected in June and July 2006 from Basket Butte (Basket Slough National Wildlife Refuge, Marion County, Oregon), Bellfountain Prairie (William L. Finley National Wildlife Refuge, Benton County, Oregon), and Oak Creek (McDonald-Dunn Research Forest, Benton County, Oregon), or obtained from local native seed producers (Landmark Seed, Albany, Oregon; Pacific Northwest Natives, Albany, Oregon; and Outsidepride.com, Inc., Independence, Oregon).
| Species | Tribe | Lifespan | Provenance | Source |
| Avena fatua | Aveneae | Annual | Exotic | Collected: Basket Butte |
| Arrhenatherum elatius | Aveneae | Perennial | Exotic | Collected: Basket Butte and Bellfountain Prairie |
| Koeleria macrantha | Aveneae | Perennial | Native | Purchased: Landmark Seed |
| Bromus hordeaceus | Bromeae | Annual | Exotic | Collected: Basket Butte |
| Bromus inermis | Bromeae | Perennial | Exotic | Purchased: Outside Pride |
| Bromus carinatus | Bromeae | Perennial | Native | Purchased: Pacific Northwest Natives |
| Cynosurus echinatus | Poeae | Annual | Exotic | Collected: Basket Butte and Oak Creek |
| Schedonorus phoenix | Poeae | Perennial | Exotic | Collected: Basket Butte |
| Festuca roemeri | Poeae | Perennial | Native | Purchased: Pacific Northwest Natives |
| Taeniatherum caput-medusae | Triticeae | Annual | Exotic | Collected: Basket Butte |
| Elymus glaucus | Triticeae | Perennial | Native | Collected: Basket Butte |
TABLE A3. Concentration of the compounds used in the fertilizer solutions(modified from Hoagland and Arnon 1938, Downs and Hellmers 1975). KH2PO4 and NH4NO3 were each supplied at concentrations equivalent to 0.2%, 1%, and 10% the concentration prescribed in a half-strength Hoagland’s recipe. While the concentration of all other nutrients remain the same, these low, medium, and “high” N and P concentrations were crossed to produce nine fertilizer solutions.
| Compound | Concentration (µM) | |
| Macronutrients | K2SO4 | 1250 |
| MgSO4·7H2O | 1000 | |
| KH2PO4 | 1, 5, 50a | |
| CaSO4·2H2O | 2000 | |
| NH4NO3 | 7.5, 37.5, 375a | |
| Micronutrientsb | KCl | 25 |
| H3BO3 | 12.5 | |
| MnSO4·H2O | 1 | |
| ZnSO4·7H2O | 1 | |
| CuSO4·5H2O | 0.25 | |
| H2MoO4·H2O | 0.25 | |
| NaFeEDDHA (6% Fe) | 10 |
a KH2PO4 and NH4NO3 are each supplied at concentrations equivalent to 0.2%, 1%, and 10% the concentration prescribed in a half-strength Hoagland’s recipe.
b All solutions, regardless of concentration of N and P, receive the same concentration of micronutrients
TABLE A4. Standardized Mantel statistic and P value of randomization test for Mantel’s tests for correlation between soil chemistry variables and ordination scores of sample units in species space.
| Soil chemistry variable | Mantel’s r | P |
| Soil moisture | -0.053 | 0.1490 |
| pH | 0.263 | 0.0010 |
| Ammonium | 0.117 | 0.0540 |
| Nitrate | 0.459 | 0.0010 |
| Total organic carbon | 0.024 | 0.2830 |
| Total nitrogen | 0.076 | 0.0770 |
| Total phosphorus | 0.431 | 0.0010 |
TABLE A5. Mean total biomass (mg) ± 1SE for each species-planting density-N level.
| Species | Density |
7.5 µmol N mean ± 1 SE |
37.5 µmol N mean ± 1 SE |
375 µmol N mean ± 1 SE |
| Arrhenatherum elatius | 1 | 88.8 ± 20 | 176.3 ± 35 | 1055.0 ± 180 |
| 10 | 28.6 ± 4 | 36.6 ± 5 | 150.9 ± 17 | |
| Avena fatua | 1 | 79.2 ± 11 | 110.2 ± 21 | 526.8 ± 130 |
| 10 | 55.2 ± 10 | 60.2 ± 9 | 99.2 ± 14 | |
| Bromus carinatus | 1 | 131.6 ± 28 | 225.9 ± 47 | 849.0 ± 150 |
| 10 | 56.5 ± 11 | 72.5 ± 14 | 183.3 ± 37 | |
| Bromus hordeaceus | 1 | 65.9 ± 11 | 162.1 ± 34 | 941.2 ± 160 |
| 10 | 18.1 ± 2 | 31.4 ± 3 | 129.8 ± 13 | |
| Bromus inermis | 1 | 74.6 ± 19 | 186.8 ± 50 | 934.8 ± 190 |
| 10 | 26.0 ± 3 | 36.4 ± 3 | 151.0 ± 18 | |
| Cynosurus echinatus | 1 | 88.1 ± 28 | 148.9 ± 37 | 1351.8 ± 290 |
| 10 | 15.3 ± 4 | 38.6 ± 10 | 175.2 ± 21 | |
| Elymus glaucus | 1 | 71.9 ± 13 | 203.2 ± 33 | 630.9 ± 140 |
| 10 | 33.4 ± 4 | 38.0 ± 5 | 112.9 ± 14 | |
| Festuca arundinacea | 1 | 99.3 ± 25 | 243.1 ± 43 | 1356.6 ± 250 |
| 10 | 26.3 ± 4 | 40.1 ± 5 | 174.1 ± 22 | |
| Festuca roemeri | 1 | 204.4 ± 54 | 269.3 ± 40 | 1059.3 ± 230 |
| 10 | 75.2 ± 15 | 92.9 ± 15 | 227.1 ± 29 | |
| Koeleria macrantha | 1 | 60.1 ± 18 | 156.1 ± 41 | 962.3 ± 190 |
| 10 | 11.0 ± 2 | 27.7 ± 4 | 136.0 ± 22 | |
| Taeniatherum caput-medusae | 1 | 71.2 ± 13 | 171.6 ± 25 | 954.4 ± 160 |
| 10 | 29.0 ± 4 | 43.6 ± 4 | 111.7 ± 13 |
TABLE A6. Mean root-to-shoot ratio ± 1 SE for each species-planting density-N level.
| Species | Density |
7.5 µmol N root:shoot ± 1 SE |
37.5 µmol N root:shoot ± 1 SE |
375 µmol N root:shoot ± 1 SE |
| Arrhenatherum elatius | 1 | 2.27 ± 0.4 | 2.09 ± 0.3 | 1.74 ± 0.3 |
| 10 | 2.81 ± 0.8 | 2.10 ± 0.3 | 2.13 ± 0.4 | |
| Avena fatua | 1 | 8.43 ± 7.6 | 0.71 ± 0.1 | 0.40 ± 0.1 |
| 10 | 0.49 ± 0.1 | 0.57 ± 0.1 | 0.53 ± 0.1 | |
| Bromus carinatus | 1 | 1.59 ± 0.3 | 1.91 ± 0.4 | 1.02 ± 0.2 |
| 10 | 1.00 ± 0.1 | 0.93 ± 0.1 | 0.91 ± 0.1 | |
| Bromus hordeaceus | 1 | 2.56 ± 0.4 | 1.70 ± 0.2 | 1.30 ± 0.2 |
| 10 | 2.98 ± 0.9 | 2.18 ± 0.6 | 1.60 ± 0.3 | |
| Bromus inermis | 1 | 2.43 ± 0.3 | 2.10 ± 0.2 | 1.95 ± 0.3 |
| 10 | 2.24 ± 0.4 | 1.89 ± 0.3 | 2.01 ± 0.4 | |
| Cynosurus echinatus | 1 | 2.11 ± 0.5 | 2.52 ± 0.6 | 1.87 ± 0.4 |
| 10 | 4.31 ± 1.6 | 2.04 ± 0.4 | 2.54 ± 0.6 | |
| Elymus glaucus | 1 | 1.79 ± 0.2 | 2.19 ± 0.4 | 1.22 ± 0.2 |
| 10 | 1.74 ± 0.4 | 1.43 ± 0.1 | 1.26 ± 0.1 | |
| Festuca arundinacea | 1 | 4.57 ± 1.8 | 2.61 ± 0.5 | 1.57 ± 0.3 |
| 10 | 3.04 ± 0.6 | 2.28 ± 0.4 | 2.05 ± 0.3 | |
| Festuca roemeri | 1 | 1.79 ± 0.4 | 1.86 ± 0.3 | 1.12 ± 0.2 |
| 10 | 2.15 ± 0.2 | 2.54 ± 0.3 | 1.86 ± 0.2 | |
| Koeleria macrantha | 1 | 2.31 ± 0.4 | 3.95 ± 1.4 | 1.73 ± 0.4 |
| 10 | 2.23 ± 0.5 | 3.38 ± 0.8 | 2.80 ± 0.9 | |
| Taeniatherum caput-medusae | 1 | 1.78 ± 0.3 | 1.64 ± 0.4 | 1.28 ± 0.3 |
| 10 | 1.42 ± 0.3 | 1.46 ± 0.3 | 1.10 ± 0.2 |
LITERATURE CITED
Downs, R. J., and H. Hellmers. 1975. Environment and the experimental control of plant growth. Academic Press, New York, New York, USA.
Hoagland, D. R., and D. I. Arnon. 1938. The water culture method for growing plants without soil. Circular / University of California, College of Agriculture, Agricultural Experiment Station.