- Author: Ryan Hill
- Author: Marcelo Moretti
Introduction:
Pollinator insects are essential to produce many economically and nutritionally important crops grown in the western USA. These crops include blueberries, almonds, sunflowers, cucurbits, and many others. Almond pollination in California plays a vital role in the apiary industry, driving beekeepers to haul huge numbers of bee colonies to California for the few weeks in late winter when almonds bloom. Bees are selective of the pollen and nectar they forage, and diverse floral resources can allow bees to forage according to their nutritional needs (Leponiemi et al. 2023). Planting pollinator habitat in natural areas, gardens, and agricultural land is one method of supporting bee health. Irrigated agricultural land in the western USA can be an excellent resource for bees during the dry summer when flowers are rarer. However, the resident weeds in these settings are often not of high nutritional quality for hungry pollinators. To make matters worse, pollinator habitat in agricultural fields can be choked out by competition from weeds. Our control plots from these studies (Figure 1) demonstrate that point effectively.
Figure 1: Control plots at all three experimental sites were extremely weedy. This sometimes meant that none of the planted species could grow, as seen in the pictures above.
Objective:
The studies described here attempt to use herbicides to improve the chances for success in pollinator habitat establishment.
Methods:
Three locations in Oregon's Willamette Valley were selected for studies. Two were hazelnut orchards watered with drip irrigation, and one was a field plot set up for sprinkler irrigation. Each location received different soil preparation. The first orchard location (Corvallis) was not tilled, and soil compaction issues were present. The second orchard location (Amity) was power-harrowed, so the top two inches of soil were loosened. The third location (Lewis-Brown Research Farm) was plowed and disked.
All three locations were seeded in the fall with a set of flowering species with potential for pollinator habitat (Table 1).
Table 1: Species and seeding rates used for pollinator habitat establishment in Oregon's Willamette Valley. |
||
Common Name |
Scientific name |
Lb/Acre |
Hairy vetch |
Vicia villosa |
60 |
Lacy Phacelia |
Phacelia tanacetifolia |
12 |
California poppy |
Eschscholzia californica |
8 |
Farewell to spring |
Clarkia amoena |
2 |
Globe Gilia |
Gilia capitata |
2 |
Sweet alyssum |
Lubularia maritima |
2 |
These species were planted in rows, and herbicide treatments were applied over the top perpendicular to planting rows (Table 2). Four herbicides were applied post-emergence, and the rest were applied one day after planting (pre-emergence). Glyphosate treatments were only included in the orchard trials. Experimental plots were set up as a randomized complete block design with four replicates, and each species was treated as a separate experiment. A crop oil concentrate at 1% v/v was included for Motiff (mesotrione) and Basagran (bentazon), while a nonionic surfactant at 0.25% was included for Matrix (rimsulfuron) and Quinstar 4L (quinclorac). All post-emergent treatments (and glyphosate) included ammonium sulfate (AMsol 1% v/v).
Table 2: Trade name, active ingredient, and rate of herbicides applied to pollinator habitat species. Pre-emergent herbicides were applied at planting, and post-emergent herbicides were applied 30 days after crop emergence. |
||
Trade name |
Active Ingredient |
Rate (product/A) |
Pre-emergent treatments |
|
|
Cornerstone Plus |
Glyphosate |
3 qt |
Alion |
Indaziflam |
4 fl oz |
Trellis SC |
Isoxaben |
21 fl oz |
Devrinol 2XT |
Napropamide |
8 qt |
Chateau SW |
Flumioxazin |
6 oz |
Prowl H2O |
Pendimethalin |
6.3 pt |
Princep |
Simazine |
4 qt |
Motiff |
Mesotrione |
6 fl oz |
Post-emergent treatments |
||
Motiff |
Mesotrione |
6 fl oz |
Matrix |
Rimsulfuron |
4 oz |
Quinstar |
Quinclorac |
12.6 fl oz |
Basagran |
Bentazon |
2 pt |
In Amity, competition from perennial grasses resulted in poor stand establishment. A grass-selective herbicide (clethodim) was used, and the site was reseeded six months after the initial planting when soil conditions were appropriate.
Results and discussion:
Site differences.
Drastic differences were seen between sites. Table 3 shows how crop coverage differed between the three sites for each species.
Coverage at the Corvallis site was deficient for all species except hairy vetch.
Several species did very well at the Amity location. Phacelia in the glyphosate plots was exceptionally well established due to glyphosate's good control of perennial grasses that were not killed by the power harrow.
Lewis-Brown (LB) plots had the best crop establishment initially. However, this location had intense pressure from perennial weeds, so the initial crop establishment did not translate to superior pollinator habitat. The plots at LB where Alion was applied produced a good stand of Canada thistle (Cirsium arvense) by the end of the trial, which the bees loved.
Table 3: Crop Coverage for each species at each location is shown here. The values reported are from the treated plots with the highest coverage. |
|||||||
% Crop coverage (Best treatment) |
Site |
Vetch |
Phacelia |
Poppy |
Gilia |
Clarkia |
Lobularia |
Plowed and Disked |
Lewis-Brown Research Farm (LB) |
100 |
100 |
75 |
84 |
97 |
98 |
Power harrow |
Amity |
55 |
81 |
47 |
47 |
34 |
47 |
No tillage |
Corvallis |
89 |
11 |
28 |
0 |
15 |
0 |
Pre-emergent treatments
Pre-emergent herbicides often had inconsistent pollinator species safety; however, several combinations seemed safe. Napropamide was safe for Phacelia, Gilia, Clarkia, and Lobularia, while flumioxazin and pendimethalin were safe for poppy (Table 5). All five species only had adequate crop establishment at two of the three locations. Hairy vetch establishment was improved by simazine applications at all three locations, but crop coverage was not significantly different from the untreated control for this species (Table 5). Figure 2 shows the treatment by species combinations that were sometimes safe versus the combinations that were consistently safe for the planted species.
At the two orchard sites, glyphosate treatments were the best for Gilia, Phacelia, and poppy establishment (Table 5).
All three trials were conducted on fine soils with organic matter content ranging from 2-7% (USDA-NCSS soil survey). The safety of pre-emergent herbicides for pollinator species establishment may vary depending on soil characteristics.
Post-emergent treatments
Post-emergent (POST) applications were challenging to evaluate for safety. Weed control efficacy was inadequate, and so often, crop establishment was not good enough to confidently assess crop injury.
One exception was hairy vetch. This species exhibited good tolerance to a post-emergent application of Basagran, a result seen at all three locations. The results from two trials suggest that Clarkia tolerated POST applications of Quinstar. Not enough data were collected to conclude the other four species. See Table 4 for crop coverage data.
Conclusions
Site preparation was an essential consideration in our study. Soil compaction and perennial weed pressure must be addressed to have a successful pollinator habitat planting. It was also clear that pre-emergent herbicides can improve habitat establishment, but safety must be adequately established. This is especially true of different soil types and environments. In California's Central Valley, pendimethalin has been seen to occasionally cause injury in poppy plantings, which is in contrast with this study.
Table 4: Spring crop coverage (%) from plots treated with post-emergent herbicides one month after planting, which happened the prior October. Missing data from Phacelia and Lobularia at LB is due to crop loss from frost injury. |
|||||||
Crop coverage (%) |
|||||||
|
Corvallis |
Amity |
LB |
|
Corvallis |
Amity |
LB |
Hairy Vetch |
|
|
|
Gilia |
|
|
|
Untreated |
29 |
28 |
98 b |
Untreated |
0 |
8 |
54 b |
Mesotrione |
21 |
3 a |
0 a |
Mesotrione |
0 |
0 |
0 a |
Rimsulfuron |
18 |
1 a |
0 a |
Rimsulfuron |
0 |
4 |
78 b |
Quinclorac |
34 |
0 a |
28 a |
Quinclorac |
0 |
0 |
6 a |
Bentazon |
50 |
26 b |
94 b |
Bentazon |
0 |
7 |
47 b |
Phacelia |
|
|
|
Clarkia |
|
|
|
Untreated |
0 |
53 ab |
|
Untreated |
3 a |
0 |
83 b |
Mesotrione |
0 |
42 ab |
|
Mesotrione |
0 a |
0 |
34 b |
Rimsulfuron |
5 |
17 a |
|
Rimsulfuron |
4 ab |
0 |
55 b |
Quinclorac |
5 |
64 b |
|
Quinclorac |
15 b |
0 |
77 b |
Bentazon |
2 |
48 ab |
|
Bentazon |
6 ab |
0 |
0 a |
Poppy |
|
|
|
Lobularia |
|
|
|
Untreated |
2 |
11 |
2 |
Untreated |
0 |
0 |
|
Mesotrione |
3 |
11 |
0 |
Mesotrione |
0 |
0 |
|
Rimsulfuron |
6 |
0 |
0 |
Rimsulfuron |
0 |
0 |
|
Quinclorac |
2 |
5 |
3 |
Quinclorac |
0 |
0 |
|
Bentazon |
2 |
9 |
0 |
Bentazon |
0 |
0 |
|
Table 5: Spring crop coverage for pre-emergent herbicide treatments applied just after planting, which happened the prior October. Phacelia and Lobularia experienced winter kill at the LB location, so reported data is coverage from December for that location. |
||||||||
Crop coverage (%) |
||||||||
|
Corvallis |
Amity |
LB |
|
Corvallis |
Amity | LB | |
Hairy Vetch |
|
|
|
Gilia |
|
|
|
|
Nontreated |
29 |
28 ad |
98 b |
Nontreated |
0 |
8 a |
54 c |
|
Glyphosate |
23 |
46 bd |
|
Glyphosate |
0 |
47 b |
|
|
Indaziflam |
6 |
3 d |
79 b |
Indaziflam |
0 |
3 a |
36 bc |
|
Isoxaben |
11 |
17 ab |
83 b |
Isoxaben |
0 |
5 a |
31 ac |
|
Napropamide |
8 |
19 ab |
91 b |
Napropamide |
0 |
38 b |
56 c |
|
Flumioxazin |
5 |
36 bd |
90 b |
Flumioxazin |
0 |
18 a |
2 c |
|
Pendimethalin |
6 |
38 bd |
98 b |
Pendimethalin |
0 |
0 a |
13 ab |
|
Simazine |
34 |
55 d |
98 b |
Simazine |
0 |
44 b |
6 ab |
|
Mesotrione |
6 |
25 abc |
0 a |
Mesotrione |
0 |
3 a |
8 ab |
|
Phacelia |
|
|
|
Clarkia |
|
|
|
|
Nontreated |
0 a |
53 bc |
96 b |
Nontreated |
3 |
0 a |
83 b |
|
Glyphosate |
11 b |
92 c |
|
Glyphosate |
5 |
34 b |
|
|
Indaziflam |
0 a |
13 ab |
90 b |
Indaziflam |
0 |
0 a |
74 b |
|
Isoxaben |
0 a |
0 a |
82 b |
Isoxaben |
0 |
8 a |
88 b |
|
Napropamide |
2 a |
81 c |
98 b |
Napropamide |
0 |
25 b |
86 b |
|
Flumioxazin |
0 a |
30 ab |
57 ab |
Flumioxazin |
0 |
5 a |
20 a |
|
Pendimethalin |
0 a |
0 a |
15 a |
Pendimethalin |
0 |
2 a |
67 b |
|
Simazine |
0 a |
75 c |
56 ab |
Simazine |
0 |
30 b |
0 a |
|
Mesotrione |
2 a |
54 bc |
99 b |
Mesotrione |
0 | 0 a | 25 a | |
Poppy |
|
|
|
Lobularia |
|
|
|
|
Nontreated |
2 a |
11 |
2 a |
Nontreated |
0 |
0 a |
70 c |
|
Glyphosate |
30 b |
42 |
|
Glyphosate |
0 |
21 ab |
|
|
Indaziflam |
2 a |
8 |
8 a |
Indaziflam |
0 |
0 a |
16 ab |
|
Isoxaben |
2 a |
3 |
69 b |
Isoxaben |
0 |
0 a |
0 a |
|
Napropamide |
6 a |
14 |
0 a |
Napropamide |
0 |
47 c |
98 d |
|
Flumioxazin |
2 a |
31 |
63 bc |
Flumioxazin |
0 |
15 a |
34 b |
|
Pendimethalin |
2 a |
40 |
64 b |
Pendimethalin |
0 |
0 a |
0 a |
|
Simazine |
0 a |
46 |
28 ac |
Simazine |
0 |
44 bc |
5 a |
|
Mesotrione |
0 a |
7 |
8 a |
Mesotrione |
0 | 3 a | 3 a |
Figure 2: Crop coverage pictures from two months after planting the Lewis-Brown research farm show that the planted species (rows) tolerated several pre-emergent herbicides (columns). A black outline surrounds successful combinations seen in at least one of the other two trials. Combinations that were never seen to be successful again are surrounded by a red outline.
References:
Leponiemi, M., Freitak, D., Moreno-Torres, M. et al. (2023). Honeybees' foraging choices for nectar and pollen revealed by DNA metabarcoding. Sci Rep 13, 14753. https://doi.org/10.1038/s41598-023-42102-4
Soil Survey Staff, Natural Resources Conservation Service, United States Department of Agriculture. Web Soil Survey. Available online at the following link: http://websoilsurvey.sc.egov.usda.gov/.
- Author: Grace Fruto, UC Davis
- Author: Trina Kleist, UC Davis
Wildflower displays threatened
Northwest of Los Angeles, springtime brings native wildflowers to bloom in the Santa Monica Mountains. These beauties provide food for insects, maintain healthy soil and filter water seeping into the ground – in addition to offering breathtaking displays of color.
They're also good at surviving after wildfire, having adapted to it through millennia. But new research shows wildflowers that usually would burst back after a blaze and a good rain are losing out to the long-standing, double threat of city smog and nonnative weeds.
A recent study led by Justin Valliere, assistant professor in the UC Davis Department of Plant Sciences, found that native wildflowers and other plants that typically flourish following a fire were, instead, replaced by invasive plants on land that received the kind of nitrogen contained in vehicle emissions.
“Many native plants in fire-prone areas rely on fire, and some are entirely dependent on it. Some are even most abundant after a fire,” said Valliere, a UC Cooperative Extension specialist in invasive weed and restoration ecology. “But we found that these fire-following species may be especially vulnerable to the combination of nitrogen pollution and invasive plants.”
That's part of the reason why native plants in these mountains have been declining.
Seeds – banked in the soil and waiting to sprout
The problem faced by native plants can be compared to a drawn-down bank account: Funds withdrawn are not being replaced.
It starts with fire, an important ecological process, Valliere said. Flames burn through plants on the surface and return their nutrients to the soil. Seeds sleeping in the ground wait for the next rain to sprout, then use those nutrients to grow.
“Plant diversity is often highest in growing seasons immediately after a site burns,” he said.
But invading plants have many advantages over native ones. They often sprout earlier, grow faster and create more seeds, all while tolerating drought.
“They're like cheaters,” Valliere said. “They don't follow the same rules.”
Nitrogen, too, is an important piece of every plant's nutrition. They all get a fertilizing boost from nitrogen that floats up in vehicle emissions and falls to the ground. But the invaders use nitrogen and other nutrients to grow faster, winning the race for water and sunlight. As a result, fewer native plants reach maturity, producing fewer seeds that keep their populations thriving.
When the bank balance reaches zero
The 2013 Springs Fire gave Valliere a unique opportunity to study the combined impacts of wildfire and extra nitrogen. He and colleagues from UC Riverside and the National Park Service created test plots in the Santa Monica Mountains where the fire had burned. Then, they added nitrogen to the soil to mimic the amount and type that LA's smog would deposit. Over the study's three years, native plants that typically would have flourished after wildfire instead declined even faster in the plots with added nitrogen.
Native seeds sprouted, but didn't flower. Over time, the soil's bank of seeds drew down.
“Each seed has one chance to flower and reproduce,” Valliere said. “If a seed grows and gets outcompeted, that seed has lost its chance to replenish the seed bank.”
Without the chance to replenish their bank account, native plants will die out, and the whole ecosystem will be thrown out of balance.
“There is inherent value in biodiversity,” Valliere said. “These invasive weeds could prevent the re-establishment of native shrubs after fire, sometimes forever altering the plant community.”
The loss of native plants can have cascading effects on the larger environment, he added. Problems can include the loss of native bees that feed on the flowers, and mudslides when rain makes hillsides unstable.
This problem is likely to repeat in similar areas where biodiversity is highest after wildfires – including parts of the Mediterranean basin, southern Africa and Australia. The addition of city smog “could have serious consequences for the biodiversity of fire-prone ecosystems worldwide,” Valliere warned.
Read the paper, “Nitrogen deposition suppresses ephemeral post-fire plant diversity,” by Justin Valliere, Irina Irvine and Edith Allen.
This article was first published on the UC Davis Department of Plant Sciences website.
/h3>/h3>/h3>- Author: Jules Bernstein, UC Riverside
How to help plants in drought-stricken states
A new UC Riverside study shows it's not how much extra water you give your plants, but when you give it that counts.
This is especially true near Palm Springs, where the research team created artificial rainfall to examine the effects on plants over the course of two years. This region has both winter and summer growing seasons, both of which are increasingly impacted by drought and, occasionally, extreme rain events.
Normally, some desert wildflowers and grasses begin growing in December, and are dead by June. A second community of plants sprouts in July and flowers in August. These include the wildflowers that make for an extremely popular tourist attraction in “super bloom” years.
“We wanted to understand whether one season is more sensitive to climate change than another,” said Marko Spasojevic, UCR plant ecologist and lead study author. “If we see an increase or decrease in summer rains, or winter rains, how does that affect the ecosystem?”
The team observed that in summer, plants grow more when given extra water, in addition to any natural rainfall. However, the same was not true in winter.
“Essentially, adding water in summer gets us more bang for our buck,” Spasojevic said.
Their findings are described in a paper published in the University of California journal Elementa.
Over the course of the study, the team observed 24 plots of land at the Boyd Deep Canyon Desert Research Center, in the Palm Desert area. Some of the plots got whatever rain naturally fell. Others were covered and allowed to receive rain only in one season. A third group of plots received additional collected rainwater.
While adding water in summer resulted in higher plant biomass, it generally did not increase the diversity of plants that grew, the researchers noted. Decreasing rainfall, in contrast, had negative effects on plants across both summer and winter, but may lead to some increased growth in the following off-seasons.
Implications of the work extend beyond learning when additional water resources might be applied simply to help plants grow. Whole communities of animals depend on these plants. They are critical for pollinators such as bees and butterflies, and they play a big role in controlling erosion and movement of soils by wind.
“Studies like this one are critical for understanding the complex effects of climate change to dryland ecosystems,” said Darrel Jenerette, UCR landscape ecologist and study co-author.
Desert plants also play an important role in removing carbon dioxide and nitrogen from the atmosphere to use as fuel for growth. Microbes that live in the soil can use the carbon and nitrogen released by plant roots, then send it back into the atmosphere where it can affect the climate.
“Drylands cover roughly a third of the land surface, so even small changes in the way they take in and emit carbon or nitrogen could have a big impact on our atmosphere,” said Peter Homyak, UCR environmental scientist and study co-author.
As the team continues this research over the next few years, they expect to see changes in soil carbon and nitrogen cycling, given that plants are already being affected by changes in seasonal rainfall, as this study shows.
“Can changes in precipitation patterns alter the feedback between plants and microbes, destabilizing the carbon locked in soils and sending more of it into the atmosphere? We are working on figuring that out,” Homyak said.
Editor's note: Jenerette and Homyak are affiliated with University of California Agriculture and Natural Resources through UC Riverside's Agricultural Experiment Station.
/h2>Fall or early spring is the best time to start a wildflower garden. Layout your design on paper and then transfer to your garden. Select the plants and type of wildflowers you want (either a wildflower mixture or buy specific plant seeds). Prepare your soil by clearing the area of existing weeds and grasses. Scrape to clear the soil (preferred) or if necessary, use herbicide at least 3 weeks before you sow your seeds. Once the ground is cleared, lightly cultivate or bow rake the area to loosen the top 1” of soil. Add amendments to the soil if needed. Most wildflowers do not root deep, so do not spend a lot of time digging and tilling your soil. Just make sure it has enough nutrients for the seeds to germinate. Scatter seeds onto the prepared soil, and then simply walk around on the area to set the seeds into the soil. Cover lightly with mulch or bark if desired.
That is all there is to planting a wildflower garden. Just sit back and wait for Mother Nature to do her best at providing you a season of color! Plant seeds for Fall, Spring and Summer and expect a colorful yard for most of the year. Some common wildflowers are lupine, Blue Flax, Poppy, Daisy, cornflower, Evening Primrose, Aster, Goldenrod, Indian blanket, coreopsis, coneflower, Cosmos. The list is almost endless; speak to your local nursery or Master Gardener for a list of wildflowers you can grow.
By Denise Seghesio Levine, U.C. Master Gardener of Napa County
Even if you are busy harvesting and giving away zucchini, picking tomatoes for salads and sauces and preserving summer's sweet fruits for winter treats, it is time to take a break and plan next year's garden. Note where you have your vegetables planted this year. Ponder where you might like new shrubs or trees. Imagine where a new patch of annuals or herbs or wildflowers might be nice.
Spring is when many of us, in a normal year at least, would be strolling garden centers for seeds and plants to provide summer color and crops. With all the weeding, watering, harvesting and preserving needed to maintain a summer garden, sometimes we forget that fall is actually a better time to plant many shrubs and seeds.
Most shrubs appreciate being relocated and planted in the fall. The temperatures are milder, and the danger of drought and heat stress is less. The new plants will appreciate having a month or two to get acclimated to a new spot and then a season of rain to help new roots stretch deep into the earth. Planting now gives new plantings a headstart in spring and usually results in healthier, stronger plants better equipped to withstand summer heat and water stress.
I have been musing on the best place for a new Philadelphus (mock orange) and some hostas a friend has offered me. And the north side of my house needs a forest of foxglove. So I have some planning to do.
Find a pad of paper or favorite notebook and a comfy spot in the garden where you can see your domain. Make a simple drawing or record of what vegetables and annual flowers you have planted now, and then figure out where you can plant those vegetables next year that is far from where they are planted now.
The point is to avoid planting the same vegetable or family of vegetables in the same place. There are a couple of reasons for this.
First, different vegetables need different nutrients. Some plants seriously deplete the soil. These heavy feeders include melons, winter and summer squashes, corn, and cole crops such as cauliflower and cabbage.
You might have noticed the soil seems to kind of disappear by the end of a growing season in some beds. You are not imagining it. The nutrients in the soil must be replaced. Replenishing the soil with compost and other amendments and following a heavy feeder with a nitrogen-fixing crop like peas or fava beans will pay dividends in healthier plants and larger harvests.
Rotating crops also helps combat cucumber beetles and other pests that attack your vegetables, then overwinter in the soil and emerge again next year just about the time your vegetable seedlings are starting to produce. There are few controls for some of these pests apart from interrupting their food source.
Fall is also the perfect time to directly sow many annual seeds for next spring. Love-in-a-mist (Nigella), cosmos, calendula, poppies, lupine, sweet peas, sweet Williams and forget me nots can be sown September through December and will brighten the garden much earlier than if sown in the spring. If you do not have seeds yet, visit your favorite garden center or order seeds online. Many seed companies have restocked since the spring, when you may have had problems finding seeds.
More immediately, if you want to grow crops from seed this fall and winter, it is time to sow lettuce, spinach, peas, broccoli, cabbages and leafy greens. Planting seeds now will produce seedlings to set out in the garden in four to six weeks. Gardening year round in Napa is a luxury. Lots of variety with less watering is a winning combination.
One final August hint: If you are growing peppers, check the leaves. They should have dark green, smooth, glossy leaves. If the leaves are bumpy or curled, they are letting you know they need bone meal. A tablespoon or two scratched around each plant and watered in each week until the plants have nice smooth leaves again will pay off in healthier plants and more peppers. Feed them regularly, or at least at the first sign of those telltale bumpy leaves. You're welcome.
Food Growing Forum: Join Napa County Master Gardeners on Sunday, August 30, from 3 p.m. to 4 p.m., for a free Zoom discussion on “Growing Winter Vegetables.” This forum on food growing will continue monthly on the last Sunday of every month, with different topics every time. To receive the Zoom link for the August 30 forum, register at http://ucanr.edu/FoodGrowingForum2020.
The UC Master Gardeners of Napa County are volunteers who provide University of California research-based information on home gardening. To find out more about home gardening, upcoming events or to submit gardening questions, visit the Master Gardener website (napamg.ucanr.edu). Our office is temporarily closed to walk-in questions but we are answering questions remotely and by phone or email. Submit your gardening questions through our website, by email mastergardeners@countyofnapa.org or leave a phone message at 707-253-4143. Master Gardeners will get back to you within a few days.