- Author: Michael D Cahn, Ph.D.
If you have an interest to receive state funding for upgrading your irrigation system to improve water use efficiency, then you may want to consider applying for SWEEP funding. Upcoming workshops on SWEEP will be in Salinas on July 14, and in Watsonville on July 15th. Please see the announcement below:
FUNDING OPPORTUNITY FOR IMPROVING FARM
WATER AND ENERGY USE EFFICIENCY!
UP TO $200K PER FARM
The California Department of Food and Agriculture (CDFA) is accepting applications for its 2016 State Water Efficiency and Enhancement Program (SWEEP) Round II. SWEEP is a competitive grants program supporting growers and agricultural operations in California to reduce their Greenhouse Gas (GHG) emissions and save water by investing in water irrigation system efficiency. Projects must reduce GHG emissions and save water. Applicants must provide supporting documentation directly related to actual, on-farm water consumption and GHG emissions during the prior growing season to be eligible for funding. Grant submission deadline is August 5, 2016, and grant-funded work must be completed by November 2017.
THE RESOURCE CONSERVATION DISTRICTS OF
MONTEREY, SANTA CRUZ and LOMA PRIETA
TO ATTEND ONE OF THE FOLLOWING
TECHNICAL ASSISTANCE WORKSHOPS TO PREPARE YOUR 2016 SWEEP PROPOSAL
6 - July
8am to 12pm
San Lorenzo Park
1160 Broadway, King City, CA
14 - July
8am to 12pm
UC Cooperative Extension
1432 Abbott St, Salinas, CA
15 - July
9am to 12pm
UC Cooperative Extension Santa Cruz County
1430 Freedom Boulevard, Suite E, Watsonville, CA
20 - July
9am to 12pm
Morgan Hill Community Center
17000 Monterey Rd., Morgan Hill, CA
These workshops will give you an overview of the program, and provide hands-on assistance with project requirements, application process and materials. You will have an opportunity to meet representatives from various companies that sell the types of irrigation supplies and equipment you can acquire with your SWEEP grant. For more details visit the program's website at https://www.cdfa.ca.gov/oefi/sweep/, or contact Ben Burgoa at email@example.com (805-717-3261) for assistance in Monterey County, or Sacha Lozano at firstname.lastname@example.org (831-224-0293) in Santa Cruz and Santa Clara Counties. Be ready! Please bring information about your irrigation system and pump characteristics to assess your farm water consumption and GHG emissions.
- Author: Michael D Cahn, Ph.D.
- Contributor: Richard Smith
The short answer is not very much (unless you are fertigating). Nitrate-N concentrations in most agricultural wells on the Central Coast range from 2 to 50 ppm. Some wells do have background levels of NO3-N as high as 70 ppm but these concentrations are uncommon.
We used an electrical conductivity (EC) meter to measure the change in salinity of well water after adding different concentrations of nitrate salts. The well water tested in our study was highly suitable for vegetable production: the EC was 0.5 dS/m and the background concentration of nitrate was 3 ppm NO3-N. We added sodium- and calcium-nitrate salts to the water to achieve concentrations of nitrate ranging from 3 to 42 ppm N.
Figure 1 shows the effect of nitrate concentration on salinity of the water. The salt content of the water did increase with increasing concentrations of NO3-N, but increases in salinity were modest. For each increase of 10 ppm NO3-N, the EC of the water was raised by 0.07 dS/m. At the highest NO3-N concentration evaluated (42 ppm N) the corresponding EC of the water averaged 0.77 dS/m, or a boost in salinity of 0.27 dS/m. Even at the highest nitrate concentration, the water that we tested was still very suitable for producing cool season vegetables and strawberries without causing yield loss.
Figure 1. Nitrate concentration effects on salinity of water.
A high concentration of nitrates in irrigation water can also supply a significant portion of the nitrogen needs of a crop. Irrigation water with an NO3-N concentration of 42 ppm would supply approximately 9.5 lbs of N/acre for each inch of water applied, or about 77 lbs of N/acre for a lettuce crop if 8 inches of water were applied during the season.
Some growers have observed that their high nitrate wells are problematic for producing good vegetable crops, and have remarked that high nitrate water tends to be salty. This study demonstrated that nitrate is probably not the cause of the salinity, unless the nitrate concentrations are very high (> 100 ppm N).
Well water can have a high salt content for a variety of reasons. Underground aquifers derived from marine sediments can contain salts that increase the salinity of groundwater. Near the coast, wells can become salty if seawater intrudes into ground water. Another source of salts is from irrigation water. Approximately 1 ton of salts are contained in an acre-foot of water that has an EC of 1.15 dS/m. As crops transpire moisture, salts accumulate in the soil, and will eventually leach deeper in the soil profile as more irrigation water is applied. Over time, leached salts could eventually reach the ground water, and increase the salinity level of the water.
In conclusion, nitrates in irrigation water are unlikely to be a significant cause of salinity of ground water. If your well water has a high concentration of nitrates and also has a high EC (> 1 dS/m), a water suitability test may reveal other salts contributing to the salinity of the water. Nitrates in the water can also be a significant source of nitrogen for your crops.
For several years the leafy greens industry has been engaged with regulatory agencies regarding the issue of cadmium (Cd) concentration in fresh produce; Cd, a heavy metal element, poses human health risks if ingested in significant quantity. The 2016 production season marks the first time that California spinach growers may be required to alter their production practices to minimize the amount of Cd taken up by this crop. Spinach is the focus of concern because it takes up much more Cd than other common vegetable crops (Fig. 1).
The graph makes clear that soil Cd content is a major factor determining crop Cd uptake. We have a general understanding about where the highest Cd soils are located, but flooding events over centuries have moved and mixed soil sediments. Therefore, soil testing is a critical step in evaluating the field-specific risk. The soil test procedure for which we have the most data is total soil Cd measured by nitric acid/hydrogen peroxide extraction. Soil samples should be taken from the top foot, which is the effective rooting depth of spinach.
In fig. 1 it is clear that individual fields differ substantially from the general trend line relating total soil Cd to tissue Cd because other factors also have influence. Those factors include:
- Variety – preliminary field evaluations suggests that tissue Cd concentration may differ among varieties by up to 25%.
- Soil pH – Cd bioavailability declines with increasing soil pH.
- Irrigation water chloride (Cl) concentration – increasing Cl concentration makes Cd more bioavailable.
- Soil zinc (Zn) level – Zn and Cd compete for plant uptake, so soil with higher Zn availability tend to have less Cd uptake.
Individual spinach shippers may impose soil Cd limits on their growers, or require remediation practices to be deployed if fields above a certain soil Cd level are used; given the uncertainties in the relationship between spinach Cd concentration to total soil Cd, different shippers may set different rules for their growers to follow.
Where growers are required to use remediation practices to reduce spinach Cd uptake, our research suggests that high-rate Zn application is the most practical approach. Zn and Cd are closely related ions, and plants are not able to distinguish well between these ions. Increasing the ratio of plant-available soil Zn to Cd suppresses Cd uptake. However, to significantly decrease Cd uptake much higher levels of Zn application are needed than would typically be used to remedy a soil Zn deficiency. Across numerous field and pot trials we have observed that applying 25-50 PPM elemental Zn on a soil dry weight basis (equivalent to approximately 100-200 lb elemental Zn per acre foot of soil) suppressed crop Cd uptake by roughly 30-60%. However, the effectiveness of Zn application was affected by the following factors:
- Zinc sulfate and zinc chelate were more effective in reducing Cd uptake than zinc oxide. Zinc sulfate was more economical than zinc chelate.
- Granular forms of zinc sulfate were less effective in reducing Cd uptake than powdered forms, or zinc solutions. We presume that Zn from the granules did not disperse thoroughly through the soil.
- To be maximally effective, Zn must be distributed throughout the primary rooting zone of spinach (the top 8-12 inches of soil). Zn distributed only in the top few inches of soil was only marginally effective.
- Disking incorporates Zn to a depth of approximately 6 inches and is therefore more effective than mulching, which incorporates Zn only to about 3 inches. Where practical, incorporation of Zn even deeper than 6 inches would be ideal.
Zinc foliar applications:
- Foliar applications of zinc sulfate or zinc chelate were not effective at reducing Cd uptake in spinach.
- When Zn is applied to soil it slowly becomes less plant-available over time, as chemical compounds of low solubility are formed. However, high-rate Zn application will have measurable effects over several years at least. In a field trial, in the first crop following application of 100 pounds of elemental Zn (280 lbs of zinc sulfate) per acre we observed a 40% reduction in Cd uptake by spinach; after two years the Zn-treated area still showed a 15% reduction in crop Cd uptake. In pot trials, when 80 PPM elemental Zn was added to high-Cd soils, the reduction in Cd uptake of four successive spinach crops was 66%, 66%, 51% and 49%. Based on these observations, it is clear that Zn applications can be effective across years, but additional Zn application may be needed to maintain maximum efficacy over the long term.
Other potential remediation practices include raising soil pH, or applying organic amendments. These practices are aimed at making soil Cd less plant-available. Increasing pH does this by precipitating Cd salts, while organic amendments like compost may tie up Cd on its complex cation exchange sites. Our preliminary data suggest that both practices can have a positive effect, but the effects are less substantial than those we observed with high-rate Zn application.
In summary, regulatory pressure is forcing the spinach industry to adopt practices to limit spinach Cd concentration before we have developed a comprehensive understanding of how best to do that. Based on our current data we believe that fields with total soil Cd below 1 PPM present relatively low risk, while those above 2 PPM will be more difficult to remediate reliably. Remediation practices can be effective in fields between 1-2 PPM total soil Cd, but results in individual fields will vary, based on the complicating factors we have outlined.
- Author: Shimat Villanassery Joseph
Recently (mid April), a large number of grasshoppers has been found attacking broccoli and spinach crops in the southern parts of Salinas Valley (San Lucas, San Ardo etc). It is believed that these grasshopper populations were migrating from the dry grassland to leafy greens and Brassica crops. The feeding damage was typically found along the edge of the fields adjacent to the hills. Also, blister beetles (Epicauta spp.) were seen along with grasshoppers. Blister beetles were mostly feeding on the weed plants surrounding the fields. The feeding damage may not be critical but these insects may contaminate the harvested produce with dead or alive bodies and their excrement. The blister beetle adult is about an inch long, and blackish blue in color. Blister beetle has a distinct look that make them easy to identify from other beetles. The width of the neck is shorter than width of the head. The outer pair of fore wing is flimsy and not held tight on the abdomen.
Ecologically, both grasshopper and blister beetle interact with each other. The larval stages of blister beetle are predaceous and often prey on the eggs of grasshopper. Grasshopper lays eggs in a pod (120 eggs maximum) below the soil. The eggs hatch to first instar nymphs which molt through six nymphal stages before develop into adults. The nymphal stages are wingless but the late nymphal stages have wing pads (incomplete wings). Nymphal stages move only by jumping whereas adults can fly and jump. Most of the grasshoppers found in the fields are nymphs and they are found in aggregation feeding on the broccoli plants. It seems like they like broccoli than spinach. Grasshoppers are migratory in nature meaning they feed on what they find on their way and as the food resource depletes, they move on to another green patch.
Because of the greater size and high mobility, it is relatively difficult to kill these grasshoppers using insecticides. In the Salinas Valley, the wee and morning hours are cooler and grasshoppers are less active and remain in the ground waiting for the day to warms up. These early day time might be the best time for insecticide application but still, they might move away when the sprayer equipment approach them. Pyrethroid insecticides and acephate are effective but multiple applications might be warranted because grasshoppers are continuously moving in from the nearby dry grassland. Please check the label instructions before selecting the insecticide for grasshopper control. Management of grasshopper using organic insecticides will be a greater challenge than synthetic insecticides. Organically approved insecticides such as pyrethrum (Pyganic) might be the option. Because grasshoppers feed on plant material, spinosad (Entrust) might be effective too. Azadirachtin (Neem products) may provide some repellency. However, success is not guaranteed with any of these insecticides. There is a protozoan, Nosema locustae -- commercially available as a bait under the brand name Semaspore. The bran bait is mixed with spores and the spores enter their body while feeding. This bait is slow acting and success may vary. Physical barrier such as fencing between field and grassland might help but a spray on the barrier might check them from progressively moving into the field. Smaller production can use row covers to prevent their access to the crops. Managing grasshoppers in the grassland with approved insecticides might slow down the migration.
- Author: Jim Correll
- Author: Steven T. Koike
A new race of the downy mildew pathogen (Peronospora farinosa f. sp. spinaciae = P. effusa) on spinach was first identified in March of 2015 in Salinas, CA, U.S. This race was able to overcome most of the race 1-15 varieties evaluated. The isolate, originally designated UA201519B, was characterized based on disease development on a standard set of differential varieties. Subsequently, isolates with the same reaction pattern on the differential set have been found in numerous locations. After careful evaluation of the significance of this development to the spinach industry, the International Working Group on Peronospora (IWGP) has denominated isolate UA201519B race Pfs: 16.
Race Pfs: 16 is able to infect the differentials Viroflay, Resistoflay, Clermont, Lazio, Pigeon, and Meerkat, but not able to infect Califlay, Campania, Boeing (Avenger), Lion, Whale, and Caladonia.
The IWGP is continuously monitoring the appearance of strains of the pathogen that deviate in virulence from the known races. In this way the IWGP aims to promote a consistent and clear communication between public and private entities, such as the seed industry, growers, scientists, and other interested parties about all resistance-breaking races that are persistent enough to survive over several years, occur in a wide area, and cause a significant economic impact.
The IWGP is located in The Netherlands and is administered by Plantum NL. The IWGP consists of spinach seed company representatives (Pop Vriend, Monsanto, RijkZwaan, Bayer, Takii, Sakata, Bejo, Enza, Syngenta, and Advanseed) and Naktuinbouw, and is supported by research centers at the University of Arkansas and the University of California Cooperative Extension (Monterey County) in the U.S. Researchers all over the world are invited to join the IWGP initiative and use the common host differential set to identify new isolates.
For more information on this subject you can contact Jim Correll (email@example.com), Steve Koike (firstname.lastname@example.org), Diederik Smilde (email@example.com), or the IWGP chairperson Jan de Visser (JandeVisser@popvriendseeds.nl).
Disease reactions of race 16 (UA201519B) observed on spinach differentials by the IWGP compiled February 2016.
aDisease reactions observed in controlled inoculation tests
by the participants of the IWGP. “+” indicates
susceptible; “-“ indicates resistant disease reaction.