- Author: Jim Wolpert - UC Davis
Soil Moisture Sensors
Tensiometers Electrical Resistance Blocks Neutron Probes Di-Electric Sensors More Info
Jim Wolpert, University of California, Davis
Soil Moisture Content
The quantity of water in soil is called the soil moisture content. After rainfall or irrigation, some water drains from the soil by the force of gravity. The remaining water is held in the soil by a complex force known as surface tension and varies depending on the amount of sand, silt, and clay. Sands, with larger particles and smaller total surface area, will hold less water than clays, which have much smaller particles and larger total surface area. The drier the soil, the greater the surface tension, and the more energy it will take for a plant to extract water.
Vineyard managers often measure soil water content as a guide to determine their irrigation timings and amounts. There are several methods for monitoring soil water content. Correlating these methods with actual inches of moisture per foot of soil is very complicated (see Recommended Links) but at the very least can help a grower to identify patterns of water use, depth of irrigation, and soil water content trends over time.
Tensiometers
A tensiometer, as its name implies, is a device for measuring soil moisture tension. The design is a simple tube with a porous cup at the lower end and a vacuum gauge on top. The tube is filled with water, sealed airtight, and placed in soil. As soil dries, water is pulled from the porous cup into the soil, creating a vacuum and causing the gauge to move. As soil continues to dry, more water is pulled out and the suction increases. As soil re-wets after a rain or irrigation, water moves back into the cup and the suction decreases. Installing tensiometers in soil requires attention to detail to obtain accurate readings (see Recommended Links for installation downloads).
Tensiometers are usually placed as a pair with the shorter tube positioned in the middle of the rooting zone (e.g., 18 inches deep) and a longer tube positioned near the bottom of the rooting zone (3 to 4 feet deep). Growers can use the difference between the two tubes to monitor water usage and determine the effective depth of irrigation. At least two stations (two tubes per station) are recommended per field, or more depending on soil variability.
Tensiometers have the advantage of being inexpensive, and easy to install, maintain, and read. They are better in fine-textured soils where good contact can be made between the porous cup and the soil. They do not work well in coarse sands where good contact may not be possible. Because the gauges are aboveground, the units are prone to damage by vineyard equipment.
Electrical Resistance Blocks
Electrical resistance blocks are also known as gypsum blocks or soil moisture blocks. They are simple devices with two electrodes embedded in a block of gypsum or other similar material. When blocks are buried in soil, water moves into or out of the block, depending on the moisture of the soil, changing the resistance between the two electrodes. Like tensiometers, gypsum blocks are cheap and easy to install. They are usually installed in at least two stations per field, at two depths, and must be installed correctly to provide accurate readings. Some block designs perform better under wet soil conditions and some correct for soil temperature. The meter used to read the blocks can be moved from field to field, but is specific to the block design (i.e., it is not a simple ohm meter). The wires aboveground are much less prone to damage by equipment compared to tensiometers.
Neutron Probe
A neutron probe uses a radioactive source for measuring soil moisture. A tube, usually made of PVC or aluminum, is installed in soil to a depth of interest and the radioactive probe is lowered into soil to measure soil moisture at as many depths as desired. The probe emits fast neutrons that are slowed by water in the soil in a way that can be calibrated to the soil water content. The probe has a significant advantage, especially for perennial crops, because access tubes are easy to install and relatively permanent. Another advantage is the reading accounts for a spherical area about 10 inches in diameter, much greater than other methods. The major limitation to this method is the probe itself; it is expensive and the presence of a radioactive source triggers requirements for operators to be trained and licensed in handling, storage, and use. In some production regions, service providers are available, usually at a fixed cost per access tube for a growing season.
Di-electric Sensors
Di-electric sensors measure the di-electric constant of soil, a characteristic that changes with changing soil moisture. A common method is called time domain reflectometry, or TDR. The theory behind how this method works is too complicated to be discussed here. The advantage of these types of systems is that they are designed to be left in place and provide continuous readings of soil moisture. The disadvantages are that the units are expensive and read soil moisture only a very small distance from the unit.
Conclusion
All measures of soil moisture suffer from the same limitation — the value of the information is dependent on the extent to which the soil where the measurements are taken reflects the rest of the field. Where soil variability is high, growers must exercise caution in relying too heavily on relatively few measurements.
Recommended Resources
Irrigation of Winegrapes, University of California
Soil moisture management, Irrometer
Soilmoisture Equipment Corporation
Irrigation Basics for Eastern Washington Vineyards, Washington State University
Reviewed by Ed Hellman, Texas AgriLife Extension and Eric Stafne, Mississippi State University
- Author: Ben Faber
Huanglongbing or Citrus Greening caused by Asian Citrus Psyllid and its associated bacterium Candidatus Liberibacter A. causes misshapened fruit and causes the fruit to have a green portion on the skin. Hence the name citrus greening. More commonly in Southern California where we have warmer winters than in the Central Valley, without the cold we can often get some green fruit. It's the cold that brings on the color of fruit. Especially fruit on the inside of the tree or on the side of the fruit not facing the sun. Also fruit that hangs on the tree and is over-mature can regreen, losing its yellow or orange color depending on lemon or orange/mandarin. In this case, we had some fruit brought into the office that was both old and has matured in our warm winter this year. So the whole tree is covered with fruit that has either green spots or green sides.
- Author: John Krist
About 500 scientists, citrus industry representatives and regulatory staff from 22 nations gathered in Florida in early February for the fourth International Research Conference on Huanglongbing. The five-day agenda featured more than 200 presentations and posters on a wide range of issues, as the global research community strives to better understand and develop improved tools for dealing with this deadly citrus disease and the pest that vectors it, the Asian citrus psyllid.
I wish I could report a breakthrough, that a sure-fire method of halting the transmission of the HLB-causing bacterium had been found or that an HLB cure or disease-resistant rootstock had been identified. Even a foolproof means of killing ACP without costly and repetitive pesticide applications would have been welcome. But breakthroughs were in very short supply.
In fact, much of the news from Florida, Brazil and other hotbeds of ACP-HLB research was grim. The best that can be said is that several promising lines of inquiry have been identified. Some might eventually lead to improved ability to manage the pest and the epidemic it spreads. Other presentations documented how difficult it is to control this disease — and how dire are the consequences of failure.
The bleakest picture comes from Florida, where the HLB epidemic has been raging for a decade.
In 2005, when HLB was first detected in Florida, the state produced 169 million boxes of citrus fruit. This year's forecast is 90 million boxes, a decline of more than 60 percent. The disease is present in every commercial grove in the state, and many growers are no longer removing symptomatic trees. Statewide, about 3.1 million trees are currently being lost each year to HLB, and only about 2.1 million are being replaced.
Production costs have doubled, largely due to the cost of enhanced nutritional programs that help extend the productive life of infected trees, and the nearly monthly applications of pesticides required to suppress the ACP population. Yet even with all that investment, the average per-tree yield has declined 40 percent. One consequence of this has been an unprecedented abandonment of no-longer-profitable groves, nearly 33,000 acres in all. Another 43,000 acres have been bulldozed.
Last year, about a third of the crop was lost to early fruit drop before harvest. The forecast is for a similar drop this year. This is a relatively recent phenomenon, possibly related to the increasing toll HLB takes on a tree as the infection progresses over time. One of the research projects described at the conference determined that within two to three months after initial infection with HLB, even symptomless trees have lost 30 to 50 percent of their root systems. By the time canopy thinning becomes apparent, 70 to 80 percent of the infected tree's root system has been destroyed. With their ability to transport water and nutrients into the canopy severely compromised, these older trees find it difficult to sustain fruit until maturity.
Other investigators have been trying to understand how the disease epidemic spreads so fast. In the Mexican lime-producing state of Colima, for example, the number of trees known to be infected with HLB went from one to 5 million in just three years.
One research team has determined that when an HLB-infected female ACP alights on a previously uninfected tree to deposit eggs, she also feeds at the egg-laying site, introducing the bacteria into the new flush. When the eggs hatch, the nymphs feed and almost immediately acquire the bacteria themselves, a phenomenon the research team dubbed an “infectious colonization event.” As soon as the nymphs mature and fly off, they're capable of infecting other trees, even though the tree where they hatched displays no symptoms and in fact may not test positive for the presence of bacterial DNA for months or even years.
This swiftness of spread makes controlling the epidemic fiendishly difficult, akin to managing an Ebola epidemic in a densely populated urban environment. Keeping the HLB infection rate low enough for growers to remain economically viable means mounting a nearly perfect campaign to suppress ACP, identify and immediately remove newly infected trees, and replant with clean trees reared in ACP-excluding hothouses.
One of the case studies described at the conference involved a 1,000-acre citrus plantation in Brazil, where management initially reduced the HLB infection rate to an “acceptable” 1 percent of the trees each year through frequent pesticide applications (two or three time a month, and again if ACP is observed), frequent HLB scouting and tree removal (four times a year) and aggressive replanting.
However, even this “success” story revealed how easily even the best management strategy can unravel. After initially declining, the HLB infection rate inexplicably began climbing again within the Brazilian plantation. Managers didn't understand why until they looked outside their grove. Within six miles they found about 500 backyard trees infected with HLB and infested with ACP. Constant reinfection from this reservoir of 500 unmanaged trees was undoing an otherwise textbook-perfect strategy for 200,000 plantation trees. The grove owners were able to regain control over the epidemic only after they received permission from the homeowners to remove about 400 of the backyard trees and extend their ACP pesticide program to the remainder.
Several presenters referred to this as the “bad neighbor” effect, and it underscores how a large-scale suppression and management program can be undone by seemingly trivial gaps that leave pockets of disease and vectors — urban plantings, abandoned groves, even organic or no-spray commercial groves — in or near the managed plantings.
Several presenters used epidemiological computer models to simulate the spread of an HLB infection throughout a citrus management area. If at least 99 percent of the growers participate in a robust management program, the modeling showed, it appears possible to keep HLB at bay and eradicate it from the control area. At 95 percent participation, it become impossible to eliminate the infection and the epidemic begins to spread, albeit slowly. At 80 percent participation, the infection rate swiftly reaches 100 percent and management is futile.
More-hopeful news came from several projects searching for tolerance of, or even resistance to, infection by the bacteria that causes HLB. Several complex hybrids of existing rootstocks show good five-year resistance to symptoms of HLB, or continue to test negative for the bacteria despite having been inoculated with it and exposed to infected psyllids. Other projects involving various grafted combinations of rootstocks and scions have also yielded trees that become infected, but in which the bacteria reproduces less well and plant growth is not as reduced. These results suggest there is more variability in the citrus genome than previously appreciated, and that production of tolerant or resistant varieties might be achieved through sophisticated conventional breeding — not just trans-species genetic modification of the sort that might alarm GMO-averse consumers.
There were also hopeful results in the search for more effective, less risky methods for killing ACP. Several research projects involved the use of customized molecules, designed to be ingested by psyllids, that suppress genes responsible for triggering production of digestive enzymes or juvenile growth hormones. In the lab, at least, these techniques significantly heightened ACP mortality, holding out promise for a species-specific, nontoxic suppression method that avoids the risk of pesticide resistance and mortality among non-target species, such as pollinators and other beneficial insects.
What does all this mean for Ventura County and its current battle against ACP?
First of all, it underscores the critical nature of the area-wide management strategy we have implemented in the Santa Clara River Valley (and will likely extend to other areas later this year). Although HLB has not yet been detected here, it inevitably will be. We have to perfect our suppression program before that; the data from Florida, Brazil and elsewhere demonstrate the futility of an HLB exclusion or management strategy that does not maintain ACP populations below detectable levels most of the time across a broad area.
We also need to address our “bad neighbor” problem, by securing removal of abandoned or no longer maintained trees regardless of whether they're in orchards, median strips, parks or urban yards.
And we probably don't have as long as we think to get our house in order. Although HLB has “officially” been detected only in a single tree in California — and not in any ACP samples collected during the HLB-detection surveying that was begun more than two years ago — one of the studies described in Florida casts doubt on this reassuring interpretation of the data.
When psyllids are collected for the HLB survey, they're tested to determine whether they contain fragments of genetic material from the HLB-causing bacteria. This requires subjecting the minute quantities in each sample to a series of 40 amplification cycles, intended to generate sufficient copies of the DNA fragments to be detectable. If the number of cycles required to generate a “positive” exceeds 36, the state deems it inconclusive — the result of lab errors, sample contamination or just random noise in the data.
If that were true, the spatial distribution of locations where survey crews collected those borderline ACP — those that indicated a “positive” HLB detection after 37 to 39 cycles —also would be random. David Bartels, an entomologist at the U.S. Department of Agriculture's Center for Plant Health Science & Technology in Texas, decided to test that.
What he found instead was that the “inconclusive” ACP collected throughout Southern California clustered in specific locations — more than a dozen of them, in San Diego, San Bernardino, Riverside and Los Angeles counties. Most of the clusters were in the vicinity of the Hacienda Heights HLB detection from 2012, but others were scattered across the LA basin, including one on the eastern end of the San Fernando Valley.
According to Dr. Bartels, data collected in Texas indicates that ACP showing similar borderline evidence of HLB infection tend to cluster around trees that conventional DNA testing has conclusively determined to be infected. The logical conclusion to be drawn from his spatial analysis, therefore, is that there are multiple probable HLB infection sites throughout Southern California. One of them is a short freeway drive from Ventura County; others are in areas where fruit loads headed for local packinghouses — loads that often transport ACP as hitchhikers — originate.
So those are the major takeaways of the Florida conference. Any solution for HLB remains years away. The disease is probably closer than we think. The odds of controlling the epidemic are worse than we anticipated. And the consequences of failure are devastating.
— John Krist is chief executive officer of the Farm Bureau of Ventura County. Contact him at john@farmbureauvc.com.
- Author: Tunyalee Martin and Chris Laning
UC Statewide IPM Program
Identifying nontarget crop and ornamental plant damage from herbicides has become much easier with the launch of a new online photo repository by the Statewide IPM Program, University of California Division of Agriculture and Natural Resources.
Herbicides applied to manage weeds may move from the site where it was applied in the air or by attaching to soil particles and traveling as herbicide-contaminated soil. When an herbicide contacts a nontarget plant, a plant it was not intended to contact, it can cause slight to serious injury. Herbicide injury also occurs when the sprayer is not properly cleaned after a previous herbicide application. Herbicide residue can be found in the spray tank, spray lines, pumps, filters and nozzles so a sprayer must be thoroughly cleaned after an application. Dry herbicide particles can be redissolved months later and cause herbicide damage to plants. Economic damage includes reduced yield, poor fruit quality, distorted ornamental or nursery plants, and occasionally plant death.
Accurately diagnosing plants that may have herbicide injuries is difficult. In many cases, herbicide symptoms look very similar to symptoms caused by diseases, nutrient deficiencies, environmental stress and soil compaction. Plant disease symptoms such as mottled foliage, brown spots or stem death and plant pests such as insects or nematodes cause foliage to yellow and reduce plant growth similar to herbicide injury.
Dr. Kassim Al-Khatib, weed science professor at UC Davis and director of the UC Statewide Integrated Pest Management Program (UC IPM), has gathered nearly a thousand photos of herbicide-damaged plants, drawn from his own and others' research. The images are cataloged to show damage that can occur from 81 herbicides in more than 14 specific herbicide modes of action, applied in the field to demonstrate the symptoms or when known herbicide spray has drifted onto the plant.
Each image is characterized with the name of the plant, mode of action of the herbicide, and notes the specific symptoms of damage. Together these photos provide a comprehensive archive of damage to over 120 different crops and ornamental plants by known herbicides, which users can easily compare with what they see in the field.
Also included in the repository is information about the modes of action of various herbicides and an index of example herbicide trade names and active ingredients. Users can learn how unintended injury from herbicide occurs from misapplication and carryover from previous crops in addition to drift and herbicide-contaminated tanks.
The repository can be found at http://herbicidesymptoms.ipm.ucanr.edu. Increased knowledge about what causes herbicide damage and how it occurs can lead to fewer cases of herbicide injury occurring through drift or herbicide-contaminated tanks. Using the repository can increase the skill to correctly identify plant damage. Correctly identifying damage as herbicide injury and not from a plant pest or nutrient deficiency can prevent unnecessary applications of pesticides or fertilizers. Fewer applications can lessen the risk of harm of pesticides and fertilizers to people and the environment.
- Author: Ben Faber
Mark Hoddle of UC Riverside Entomology Department has intorduced a second species of natural enemy of Asian Citrus Psyllid (ACP), Diaphoencyrtus aligarhensis, imported from Punjab, Pakistan. It was officially released December 16, 2014 at the Biological Control Grove at UCR. It is anticipated that this natural enemy will be complimentary to Tamarixia radiata, a parasatoid that also attacks ACP nymphs that was released in California in 2011. It's thought that it might occupy slightly different environments where it might be more successful than Tamarixia.