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Low-Input New Groundcover and Native Grass Species for Turfgrass Replacement in the Low Desert Kai Umeda and Worku Burayu University of Arizona December 2016 Objectives: Evaluate and compare the adaptation and performance of native grass species and a new groundcover, Kurapia (Lippia nodiflora), in the southwest United States low desert arid region as a low input turfgrass replacement in non-play areas of golf courses. Generate local research-based information on the feasibility of growing Kurapia and the native grass species by properly assessing their interactions with insect pests and weeds, water and fertility requirements. Increase the awareness of stakeholders about the characteristics of Kurapia and native grass species for low water use requirements and potential water saving capacity. Start Date: 2016 Project Duration: 3 years Total Funding: $45,000 Golf courses in the southwest United States are affected by poor water quality and quantity for managing turfgrasses. To reduce water use on golf courses, the use of lesser input plant species in golf course landscapes is gaining interest. This project investigates native grass species and a new groundcover as a low input turfgrass replacement in non-play areas of golf courses. Eleven plant species were evaluated - nine grass species, a native forb, and an introduced horticultural groundcover (Table 1). Eight grasses are native to the southwest and one is an introduced forage grain from Africa. A laboratory experiment was conducted to determine the germination rate of the seeds of plant species. Two field trials were conducted and plant species seeded in 6 ft by 6 ft plots arranged in a randomized complete block design with three replicates in non-play areas of two golf courses: Camelback Golf Club in Scottsdale, AZ planted on 31 May 2016 and Whirlwind Golf Club planted on 1 June 2016 in Chandler, AZ. Field plots were installed with overhead sprinkler irrigation to deliver optimal daily water to germinate and establish the crop stands. Data were collected for: laboratory germination; weekly field plant emergence; plant height, percent ground cover; and overall plant quality for color and vigor. In the laboratory, Eragrostis tef (teff), Eragrostis intermedia (plains lovegrass), and Hilaria rigida (big galleta) began to germinate within 24 hours (Figure 2). Sporobolus cryptandrus (sand dropseed), Sporobolus airoides (alkali sacaton) and Muhlenbergia asperifolia (alkali muhly) began to germinate within 48 hours. Teff and plains lovegrass had germination rates of over 76%; Bouteloua gracilis (blue grama) exhibited 40% germination; and sand dropseed, big galleta, alkali sacaton and alkali muhly showed less than 10% germination 2016-14-564 87 of 269

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Page 1: 2016-14-564 - Michigan State University Librariesarchive.lib.msu.edu/tic/ressum/2016/87.pdfDecember 2016 . Objectives: ... At Camelback, teff emerged within 3-5 days and there was

Low-Input New Groundcover and Native Grass Species for Turfgrass Replacement in the

Low Desert

Kai Umeda and Worku Burayu

University of Arizona

December 2016

Objectives:

Evaluate and compare the adaptation and performance of native grass species and a new

groundcover, Kurapia (Lippia nodiflora), in the southwest United States low desert arid

region as a low input turfgrass replacement in non-play areas of golf courses.

Generate local research-based information on the feasibility of growing Kurapia and the

native grass species by properly assessing their interactions with insect pests and weeds,

water and fertility requirements.

Increase the awareness of stakeholders about the characteristics of Kurapia and native grass

species for low water use requirements and potential water saving capacity.

Start Date: 2016

Project Duration: 3 years

Total Funding: $45,000

Golf courses in the southwest United States are affected by poor water quality and quantity

for managing turfgrasses. To reduce water use on golf courses, the use of lesser input plant

species in golf course landscapes is gaining interest. This project investigates native grass

species and a new groundcover as a low input turfgrass replacement in non-play areas of golf

courses. Eleven plant species were evaluated - nine grass species, a native forb, and an

introduced horticultural groundcover (Table 1). Eight grasses are native to the southwest and

one is an introduced forage grain from Africa. A laboratory experiment was conducted to

determine the germination rate of the seeds of plant species. Two field trials were conducted

and plant species seeded in 6 ft by 6 ft plots arranged in a randomized complete block design

with three replicates in non-play areas of two golf courses: Camelback Golf Club in

Scottsdale, AZ planted on 31 May 2016 and Whirlwind Golf Club planted on 1 June 2016 in

Chandler, AZ. Field plots were installed with overhead sprinkler irrigation to deliver optimal

daily water to germinate and establish the crop stands. Data were collected for: laboratory

germination; weekly field plant emergence; plant height, percent ground cover; and overall

plant quality for color and vigor.

In the laboratory, Eragrostis tef (teff), Eragrostis intermedia (plains lovegrass), and Hilaria

rigida (big galleta) began to germinate within 24 hours (Figure 2). Sporobolus cryptandrus

(sand dropseed), Sporobolus airoides (alkali sacaton) and Muhlenbergia asperifolia (alkali

muhly) began to germinate within 48 hours. Teff and plains lovegrass had germination rates

of over 76%; Bouteloua gracilis (blue grama) exhibited 40% germination; and sand

dropseed, big galleta, alkali sacaton and alkali muhly showed less than 10% germination

2016-14-564

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within 7 days. Bouteloua dactyloides (buffalograss), Sporobolus contractus (spike dropseed),

and the forb Zinnia acerosa (desert zinnia) failed to germinate within 21 days under room

temperature conditions.

Field experiments showed all plant species except desert zinnia establishing a stand at

Camelback Golf Club. At Whirlwind Golf Club, all species, except teff, failed to emerge or

to establish. At Camelback, teff emerged within 3-5 days and there was better than 60%

stand establishment at 1 week after seeding (WAS) (Figure 3). Big galleta emerged over a 3-

week period to establish a 40% stand. Buffalograss and the dropseeds were very slow to

establish a stand. Most of the grasses and Kurapia, that was plugged, covered the surface

area of the plots within 5 to 8 WAS (Figure 4). Sand dropseed, plains lovegrass, and teff

grew to a height of more than 25 inches at 8 WAS (Figure 5). Kurapia and buffalograss grew

no more than 2 and 5 inches in height, respectively. Before first mowing in early July, all

plant species exhibited good quality and vigor. Late summer observations showed that

Kurapia was very aggressive and vigorous as a groundcover. All of the native grasses

performed at varying and acceptable levels to establish and provide surface area coverage

throughout the late summer (Figure 6).

Summary Points:

- Nine native and two non-native plant species were evaluated to provide ground cover

under sprinkler irrigation.

- All plant species, except desert zinnia, emerged and established well under field

conditions.

- Grasses and groundcovers germinated, established, and provided varied surface area

coverage.

- Kurapia exhibited the most vigorous and aggressive growth when grown from plugs

under optimal irrigation.

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Table 1. List of native grasses and groundcovers evaluated in the low

desert Arizona at Camelback Golf Club, Scottsdale, AZ, 2016.

Common name Scientific name Seed rate/Acre

Alkali sacaton Sporobolus airoides 3.0 lb

Alkali muhly Muhlenbergia asperifolia 1.2 lb

Blue grama Bouteloua gracilis 4.0 lb

Buffalograss Bouteloua dactyloides 218 lb

Teff Eragrostis tef 5.0 lb

Plains lovegrass Eragrostis intermedia 1.00 lb

Big galleta Hilaria rigida 174 lb

Sand dropseed Sporobolus cryptandrus 1.0 lb

Spike dropseed Sporobolus contractus 1.0 lb

Desert zinnia Zinnia acerosa 2.2 lb

Kurapia Lippia nodifora 43,560 plugs*

*Kurapia plugs planted on 12-inch spacing in 6 ft by 6 ft plots.

Figure 1. Performance of native grasses and groundcovers under sprinkler irrigation at 7

weeks after seeding (WAS) in Scottsdale, Arizona, 2016.

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Figure 2. Determination of native grasses seed germination rates in the laboratory at intervals

of days after seeding (DAS), June 2016.

0

10

20

30

40

50

60

70

80

90

See

d g

erm

inat

ion

(%

)

Seed germination in the laboratory at room temperature

1DAS 2DAS 3DAS 7DAS

Figure 3. Germination and emergence of 10 plant species in the field for 4 weeks

after seeding (WAS) to establish a stand.

0

2

0

4

0

6

0

8

0

10

0

Sta

nd

est

abli

shm

ent

(%)

Native grasses stand establishment after

seeding Camelback Golf Club, Scottsdale,

AZ, 2016

1

WAS

2

WAS

3

WAS

4

WAS

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Figure 4. Performance of 11 plant species to provide ground surface coverage at intervals of

weeks after seeding (WAS). Kurapia was planted as plugs.

0

20

40

60

80

100

Gro

un

d c

over

(%

)

Native grasses and goundcovers providing ground surface coverage

Camelback Golf Club, Scottsdale, AZ, 2016

5 WAS 6 WAS 7 WAS 8 WAS

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Figure 5. Native grasses and kurapia groundcover heights before first mowing.

0

5

10

15

20

25

30

35

40

2 WAS 3 WAS 4 WAS 5 WAS 6 WAS 8 WAS

Pla

nt

hei

gh

t (i

nch

es)

Weeks after seeding

Native grasses and groundcover height at intervals after planting

Camelback Golf Club, Scottsdale, AZ, 2016

Blue GramaAlkali MuhlySpike dropseed Teff

KurapiaAlkali SacatonPlain lovegrass

BuffalograssBig galletaSand dropseed

Figure 6. Native grasses and groundcover appearance at intervals during the late summer

following three mowing events.

0

1

2

3

4

5

6

7

8

9

10

Qu

alit

y r

atin

g (

1-9

)

Plant species during late summer

Native grasses and groundcover quality, color, and

vigor Camelback Golf Club, Scottsdale, AZ,

2016 9/6/16 10/3/16 11/15/16

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Figure 7. Native grasses and groundcover performance under sprinkler irrigation at 4 weeks

after a third mowing on 12 October 2016 and under deficit irrigation at once per week.

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