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<strong>April</strong>/<strong>May</strong> <strong>2021</strong><br />
How Much Nitrogen Can You Expect<br />
from <strong>Organic</strong> Fertilizers and Compost?<br />
Understanding the Economics<br />
of <strong>Organic</strong> Seed Production<br />
How to Help Endangered Pollinators<br />
Biosolarization and Cover Crop<br />
Impact on Weeds and Soilborne Pathogens<br />
An All New Daily Radio Show<br />
Available now on the MyAgLife App, Download Today<br />
Volume 4: Issue: 2<br />
(Photo courtesy Stephanie<br />
McKnight/Xerces Society.)
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Melissa Steidlmayer<br />
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2 <strong>Organic</strong> <strong>Farmer</strong> <strong>April</strong>/<strong>May</strong> <strong>2021</strong><br />
Scan to Watch Our Video<br />
msteidlmayer@agromillora.com
IN THIS ISSUE<br />
PUBLISHER: Jason Scott<br />
Email: jason@jcsmarketinginc.com<br />
EDITOR: Marni Katz<br />
ASSOCIATE EDITOR: Cecilia Parsons<br />
Email: article@jcsmarketinginc.com<br />
PRODUCTION: design@jcsmarketinginc.com<br />
Phone: 559.352.4456<br />
Fax: 559.472.3113<br />
Web: www.organicfarmingmag.com<br />
4<br />
10<br />
14<br />
20<br />
24<br />
How Much Nitrogen Can You<br />
Expect from <strong>Organic</strong> Fertilizers<br />
and Compost?<br />
Understanding the Economics<br />
of <strong>Organic</strong> Seed Production<br />
Biosolarization and Cover Crop<br />
Impact on Weeds and Soilborne<br />
Pathogens<br />
USDA Passes Final Rules on<br />
Hemp Growing<br />
Research into Alfalfa Crop<br />
Rotation for <strong>Organic</strong> Tomatoes<br />
14<br />
CONTRIBUTING WRITERS<br />
& INDUSTRY SUPPORT<br />
Danita Cahill<br />
Contributing Writer<br />
Taylor Chalstrom<br />
Assistant Editor<br />
Daniel Geisseler<br />
UCCE Nutrient<br />
Management<br />
Specialist<br />
Sabrina Halvorson<br />
Contributing Writer<br />
Timothy Jacobs<br />
Risk Management<br />
Specialist, USDA<br />
Neal Kinsey<br />
Kinsey Ag Services,<br />
Contributing Writer<br />
Patricia Lazicki<br />
UC Davis PhD<br />
Candidate<br />
Margaret Lloyd<br />
UCCE Small Farms<br />
Advisor<br />
Joji Muramoto<br />
UCCE <strong>Organic</strong><br />
Production Specialist<br />
Kiki Hubbard<br />
<strong>Organic</strong> Seed Alliance<br />
Richard Smith<br />
UCCE Vegetable<br />
Production Specialist<br />
Ashraf M. Tubeileh<br />
Cal Poly, San Luis<br />
Obispo<br />
26<br />
30<br />
36<br />
Food Safety Laws and Standard<br />
Operating Procedures for Urban<br />
<strong>Farmer</strong>s<br />
How to Help Endangered<br />
Pollinators While Also Helping<br />
Your Farm<br />
USDA National <strong>Organic</strong> Program<br />
Changing Approach to<br />
<strong>Organic</strong> Oversight in India<br />
26 UC COOPERATIVE EXTENSION<br />
ADVISORY BOARD<br />
Surendra Dara<br />
UCCE Entomology and<br />
Biologicals Advisor, San Luis<br />
Obispo and Santa Barbara<br />
Counties<br />
Kevin Day<br />
County Director/UCCE<br />
Pomology Farm Advisor,<br />
Tulare/Kings Counties<br />
Elizabeth Fichtner<br />
UCCE Farm Advisor,<br />
Tulare County<br />
Katherine Jarvis-Shean<br />
UCCE Area Orchard Systems<br />
Advisor, Sacramento,<br />
Solano and Yolo Counties<br />
Steven Koike<br />
Tri-Cal Diagnostics<br />
Jhalendra Rijal<br />
UCCE Integrated Pest<br />
Management Advisor,<br />
Stanislaus County<br />
Kris Tollerup<br />
UCCE Integrated Pest<br />
Management Advisor,<br />
Parlier<br />
Mohammad Yaghmour<br />
UCCE Area Orchard Systems<br />
Advisor, Kern County<br />
38<br />
Micronutrients: Effective<br />
Measurement and Use of<br />
Manganese<br />
30<br />
The articles, research, industry updates,<br />
company profiles, and advertisements in this<br />
publication are the professional opinions of<br />
writers and advertisers. <strong>Organic</strong> <strong>Farmer</strong> does<br />
not assume any responsibility for the opinions<br />
given in the publication.<br />
<strong>April</strong>/<strong>May</strong> <strong>2021</strong> www.organicfarmermag.com 3
How Much N Can You Expect from<br />
ORGANIC FERTILIZERS<br />
AND COMPOST?<br />
By MARGARET LLOYD | UCCE Small Farms Advisor<br />
DANIEL GEISSELER | UCCE Nutrient Management Specialist<br />
PATRICIA LAZICKI | UC Davis PhD Candidate<br />
JOJI MURAMOTO | UCCE <strong>Organic</strong> Production Specialist<br />
and RICHARD SMITH | UCCE Vegetable Production Specialist<br />
Nitrogen (N) is an essential plant<br />
nutrient, providing the building<br />
blocks for plant growth and development.<br />
The N sources on an organic<br />
farm are numerous, including crop<br />
residue, compost, fertilizers, soil organic<br />
matter and irrigation water (Figure 1).<br />
Nitrogen management in organic systems<br />
is challenging because complex organic<br />
forms of N originating from organic<br />
materials need to be mineralized by microbes<br />
to become plant-available mineral<br />
forms of N: ammonium (NH4+) and<br />
nitrate (NO3-). Learning how to predict<br />
and monitor N release from soil amendments<br />
are important skills useful for<br />
selecting amendments and determining<br />
application rates and timing to achieve<br />
optimum plant health and yield.<br />
Soil microbes facilitate N availability in<br />
organic systems through organic matter<br />
decomposition. Microbes use carbon<br />
(C) as their primary energy source. However,<br />
to grow, microbes also require N.<br />
When compost and fertilizers are added<br />
to moist soil, microbes are “fed” and<br />
microbial activity is stimulated. With<br />
this activity, there is rapid turnover<br />
of microbes as well as organic matter<br />
decomposition, which become the two<br />
main sources of available N for plants.<br />
However, as the ratio of C:N in the<br />
amendments approaches 20:1, additional<br />
N is required to facilitate microbial<br />
breakdown. This additional N is taken<br />
Figure 1. An example of N uptake and N supply in an organic tomato field. Field studies<br />
occurred in the Sacramento Valley in a silt loam soil with approx. 1% organic matter content,<br />
growing fresh market tomato cv Brandywine. Cover crop was an oat legume mix with 3% N<br />
that averaged approximately 3 T/A biomass that was incorporated one month before planting.<br />
Granular fertilizer was applied at 700 lb./acre. Irrigation water total estimated 3.6 acre-feet with<br />
a concentration of 1 ppm NO 3<br />
-N (Geisseler et al., unpublished).<br />
Cumulative N release/ uptake<br />
(lbs/acre)<br />
250<br />
200<br />
150<br />
100<br />
50<br />
Irrigation water<br />
Granular fertilizer (4% N)<br />
Poultry manure compost<br />
Cover crop<br />
Soil (0-24 in)<br />
Plant uptake<br />
Apr <strong>May</strong> Jun Jul Aug Sep<br />
from the pool of plant-available forms<br />
of N in the soil. Because this reduces<br />
the amount of N available to plants, it is<br />
sometimes referred to as “tying up N” or<br />
N immobilization. Because most amendments<br />
available to organic farmers are<br />
bound in complex molecules containing<br />
both C and N, only a portion of the N<br />
becomes available to plants in the short<br />
term. This begs the question, how much<br />
N can you expect from organic fertilizers<br />
and compost?<br />
What to Expect<br />
Composts, manures and organic fertilizers<br />
are all applied to supplement soil N.<br />
The N availability from these materials<br />
differs widely, from 90% to tying up<br />
N. To better understand this, we mixed<br />
common soil amendments with organically-managed<br />
field soil and incubated<br />
them for 84 days in warm and moist soil<br />
(73 degrees F and 60% water holding<br />
capacity.) Figure 2 (see page 5) shows<br />
how quickly N became available from<br />
each material. A negative value indicates<br />
4 <strong>Organic</strong> <strong>Farmer</strong> <strong>April</strong>/<strong>May</strong> <strong>2021</strong>
Figure 2. Predicted N release curves from different amendment types when<br />
incorporated into warm, moist soil 2 .<br />
Figure 3. Relationship between potentially available N<br />
and amendment carbon to nitrogen ratio 2 .<br />
Available N<br />
(% amendment N)<br />
100<br />
80<br />
60<br />
40<br />
20<br />
0<br />
0<br />
Guano<br />
Blood & feather meal<br />
Liquids<br />
Granular fertilizer, 4% N<br />
Composted poultry manure<br />
Composted yard trimmings<br />
20 40 60 80<br />
Available N @ 12 weeks<br />
(% amendment N)<br />
Available N @ 12 weeks<br />
(% amendment N)<br />
90<br />
70<br />
50<br />
30<br />
10<br />
0<br />
0<br />
5:1<br />
10:1<br />
Liquids<br />
Blood & feather meal<br />
Granular fertilizers and guano<br />
Manure composts<br />
Yard trimmings composts<br />
Carbon to nitrogen ratio<br />
%N not a good predictor<br />
for mineralization from<br />
liquids<br />
N risks being<br />
immobilized<br />
15:1 20:1<br />
Days after incorporation<br />
0 5 10 15<br />
Nitrogen concentration (%)<br />
N immobilization. Actual N release rates<br />
in the field will depend on soil moisture<br />
and temperature but will follow a similar<br />
pattern.<br />
Our research along with dozens of other<br />
studies has found that the C:N ratio and<br />
% N of an amendment are good predictors<br />
of N availability. The lower the C:N<br />
ratio in the material, the more quickly N<br />
will be released. As the C:N ratio exceeds<br />
15:1, available N moves closer to 0 due to<br />
temporarily tying up N. Such materials<br />
should not be applied too close to planting.<br />
Especially for compost, it is important<br />
to find out the total N and C:N ratio<br />
from the supplier to understand whether<br />
this material will be contributing N or<br />
tying up N in the soil. When C:N ratio<br />
is unavailable, the total N concentration<br />
is closely related to availability. Generally,<br />
as total N increases, availability of N<br />
increases (See Figure 3).<br />
Among the amendments tested, guano<br />
had a very high N content (% N) and a<br />
very low C:N ratio which resulted in high<br />
N availability (80% to 90% of the total N)<br />
and rapid availability—more than 50% of<br />
Continued on Page 6<br />
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<strong>April</strong>/<strong>May</strong> <strong>2021</strong> www.organicfarmermag.com 5
Continued from Page 5<br />
the N was available immediately with an<br />
additional 30% to 40% becoming available<br />
over 40 days (Figure 2, see page 5).<br />
On the other hand, composted yard<br />
trimmings had low total N content, less<br />
than 2%, and a high C:N ratio between<br />
13 to 20, which resulted in slight N<br />
immobilization to 4% N release.<br />
Low C:N ratio materials like guano,<br />
feather meal and fish emulsion released<br />
much of their N in the first week, and<br />
almost all their N within three weeks.<br />
This quality makes them good sidedress<br />
materials. They can also be used to<br />
remediate known N deficiency.<br />
Table 1. Potential N availability from different types of organic amendments under warm, moist<br />
conditions. Negative numbers mean the compost tied up soil N2. All % N numbers for solid<br />
amendments are on a dry weight basis. Note: Liquid % N is reported on a fresh weight basis and<br />
isn’t a good indicator of the release rate. *(See Figure 3, page 5)<br />
Municipal yard trimmings<br />
compost<br />
Poultry manure composts<br />
Granular fertilizers<br />
(except guano)<br />
Blood & feather meal<br />
Liquid fertilizers<br />
Guano<br />
Material<br />
Typical<br />
%N<br />
0.5-2<br />
2-5<br />
2-7<br />
13-15<br />
2-4*<br />
12-13<br />
Typical C:N<br />
ratio<br />
13-20<br />
6-8<br />
5-7<br />
3-4<br />
4-6<br />
3-4<br />
N available<br />
after 12 weeks<br />
-3% - 4%<br />
30 - 35%<br />
38 - 60%<br />
65 - 70%<br />
50 - 100%<br />
80 - 90%<br />
Releases in:<br />
Years<br />
Weeks-months<br />
Days-weeks<br />
Days<br />
Days<br />
Days<br />
Poultry manure composts and granular<br />
fertilizers contributed some available N<br />
as soon as they were applied, but released<br />
their N more slowly. When incorporated<br />
into moist soil under warm conditions,<br />
they will release more quickly, though<br />
still over weeks, not days (See Table 1).<br />
High C:N materials like plant-based yard<br />
trimmings and composts released little<br />
to no N. They provide C which supports<br />
microbial communities and, over time,<br />
improves soil physical structure, but<br />
provides little N in the short term. Longterm<br />
soil fertility may be improved.<br />
Plant-based liquid fertilizers ranged<br />
from 48% to 92% N availability whereas<br />
manure-based liquid fertilizers (typically<br />
fish) ranged from 83% to 99% N availability<br />
after four weeks 1,2 . <strong>Organic</strong> liquid<br />
fertilizers are suspensions and often<br />
include particulate matter with which<br />
8% to 21% of total N content is associated.<br />
Without proper filtration, these<br />
materials increase the risk of clogging<br />
drip emitters. If they are injected before<br />
the filter, a significant amount of the N<br />
can be removed from the suspension.<br />
Regular backflushing may be required to<br />
maintain system flow. New technology in<br />
liquid organic fertilizer is now providing<br />
materials in which N is thoroughly<br />
dissolved and does not have the issues<br />
just discussed. Coupled with the high<br />
cost per unit N, liquid fertilizers are often<br />
viewed as an easy way to supplement<br />
in-season fertility, but too expensive to<br />
provide the bulk of the crop’s N demand.<br />
In all cases, amendment N release is<br />
slower in cool weather or dry conditions<br />
as microbial activity is decreased. Crops<br />
planted in cold temperatures may benefit<br />
from starter fertilizers that contain some<br />
available N initially − those with a higher<br />
amount at day 0 and a steep initial curve<br />
(Figure 2, see page 5). For example, manure-based<br />
composts have roughly 15%<br />
of their total N available at application,<br />
whereas granular fertilizers started with<br />
an average of about 22%, or guano at<br />
more than 50%.<br />
If only a portion of the total N becomes<br />
available, what happens to the rest?<br />
The unmineralized organic N becomes<br />
part of the soil organic matter pool of<br />
N, and will be available in the future as<br />
the material is subject to mineralization<br />
processes.<br />
How Much N and When?<br />
Crop N demand and yield are very closely<br />
linked. The crop N demand includes N<br />
requirements to produce the plant material,<br />
harvested crop and cull produce. Expected<br />
yield is a good starting point for<br />
estimating how much N the crop needs.<br />
Specific crop N demand guidelines can<br />
be found at geisseler.ucdavis.edu/Guidelines/Home.html.<br />
The timing of crop demand depends on<br />
the crop. Figure 4 (see page 8) shows<br />
the N demand curve for broccoli tomato<br />
and strawberry. The steep areas on the<br />
curve indicate high N demand and represent<br />
times when N should be in high<br />
and sufficient supply. The fresh market<br />
tomato curve shows that from full bloom<br />
to early harvest, tomatoes utilize 73%<br />
of the crop’s total N demand. During<br />
this period, N uptake rates averaged 3<br />
to 5 pounds N/A/day. Little N was used<br />
prior to flowering or once harvest was<br />
on-going, in this case of indeterminate<br />
tomatoes. Crops with similar growth and<br />
fruiting habits form similarly shaped N<br />
demand curves, though additional crops<br />
can be found at geisseler.ucdavis.edu/<br />
Guidelines/N_Uptake.html.<br />
To ensure that sufficient N is available<br />
for the period of high N demand, taking<br />
a soil test a couple of weeks prior to that<br />
period is recommended. Samples taken<br />
at this time will reflect current availability<br />
from any number of organic sources<br />
(fertilizers, compost, cover crop residue,<br />
soil organic matter and others). Convert<br />
soil test data to lb./A to determine<br />
whether the supply will meet the demand.<br />
Details on how to take a soil sample can<br />
be found at geisseler.ucdavis.edu/Guidelines/Soil_Sampling_Nitrate.pdf.<br />
Conclusion<br />
Supplying a crop with sufficient N is<br />
essential for optimum health and production.<br />
In organic production, this is<br />
very challenging and requires the ability<br />
to synthesize hard numbers, educated<br />
Continued on Page 8<br />
6 <strong>Organic</strong> <strong>Farmer</strong> <strong>April</strong>/<strong>May</strong> <strong>2021</strong>
Continued from Page 6<br />
guesses, and keen observations.<br />
Here are some tips:<br />
• Establish an N goal for your crop.<br />
• Identify the C:N ratio or total % N of your<br />
amendment to estimate N availability for your<br />
amendment (Table 1, see page 6, Figure 3, see<br />
page 5).<br />
• Familiarize yourself with the N release pattern<br />
from amendments (Figure 2, see page 5).<br />
• Learn the N uptake demand for your crop (Figure<br />
4).<br />
• Monitor N with soil sampling to refine your estimations<br />
and confirm sufficient N for your crop.<br />
<strong>Organic</strong> N management is challenging, so we hope<br />
this article will help you navigate this important<br />
decision with more confidence and success.<br />
Additional Resources<br />
N dynamics in field-grown organic heirloom tomatoes:<br />
ucanr.edu/sites/SFA/files/343252.pdf<br />
Practical Training on N Planning and Management<br />
in <strong>Organic</strong> Production: ccsmallfarms.ucanr.edu/<br />
Events_and_trainings/Nitrogen_Planning_and_<br />
Management_in_<strong>Organic</strong>_Production_of_Annual_Crops_915/<br />
References<br />
1 Hartz, T..K., Smith, R., Gaskell, M., 2010. Nitrogen availability<br />
from liquid organic fertilizers, HortTechnology 20(1),<br />
169-172.<br />
2Lazicki, P., Geisseler, D., Lloyd, M., 2020. Nitrogen mineralization<br />
from organic amendments is variable but predictable.<br />
Journal of Environmental Quality 49, 483-495. Available<br />
at: https://acsess.onlinelibrary.wiley.com/doi/epdf/10.1002/<br />
jeq2.20030<br />
3Hartz, T.K., Cahn, M.D., Smith, R.F., 2017. Efficient nitrogen<br />
fertility and irrigation management of cool-season vegetables<br />
in coastal California. Available at: https://vric.ucdavis.edu/<br />
pdf/fertilization/fertilization_EfficientNitrogenManagementforCoolSeasonvegetable2017.pdf<br />
Comments about this article? We want to hear from<br />
you. Feel free to email us at article@jcsmarketinginc.<br />
com<br />
Crop N uptake (lb N/acre)<br />
Crop N uptake (% of total)<br />
400<br />
300<br />
200<br />
100<br />
Crop N uptake (% of total)<br />
0<br />
0<br />
100<br />
60<br />
40<br />
20<br />
0<br />
0<br />
100<br />
80<br />
60<br />
40<br />
20<br />
0<br />
0<br />
Broccoli<br />
Broccoli seeded in<br />
summer starts<br />
growing and taking<br />
up N quickly. Uptake<br />
starts to slow wjen<br />
the weather cools.<br />
20 40 60<br />
Tomato, fresh market<br />
30<br />
60<br />
Full<br />
bloom<br />
Broccoli seeded in winter<br />
only starts to rapidly<br />
take up N when the<br />
weather warms. N<br />
uptake is high right<br />
through to harvest.<br />
Days after Planting<br />
Green fruit<br />
80 100 120 140<br />
Harvest period<br />
60 90 120<br />
Days after Planting<br />
Harvest<br />
period<br />
0<br />
120 180 240 300 360<br />
Days after Planting<br />
200<br />
150<br />
100<br />
50<br />
0<br />
150<br />
Figure 4. Example of crop N uptake curves of fresh market ‘Brandywine’<br />
tomato and broccoli. Broccoli data is from a conventional field in the Salinas<br />
Valley. Yields were 28,000 and 22,000 lb./acre for summer- and winter-seeded<br />
broccoli, respectively 3 . Tomato data is from a fresh-market organic heirloom<br />
trial in Yolo County. Total yield was 62,000 lb./acre (unpublished data).<br />
160<br />
120<br />
80<br />
40<br />
Crop N uptake (lb N/acre)<br />
Crop N uptake (lb N/acre)<br />
8 <strong>Organic</strong> <strong>Farmer</strong> <strong>April</strong>/<strong>May</strong> <strong>2021</strong>
CONVERTING SOIL TEST DATA TO LB/A<br />
L<br />
Soil test results are often reported as either NO3-N or NO3 and in ppm or mg/kg. NO3-N is reporting<br />
just N whereas NO3 is reporting the whole molecule and needs to be adjusted (See conversion too).<br />
1 mg/kg = 1ppm<br />
If soil test is NO3, convert to NO3-N: ppm / 4.42 =<br />
NO3<br />
ppm<br />
NO3-N<br />
Converting ppm or mg/kg to lb./acre can be calculated by multiplying this number by a factor of<br />
three to four per 12’’ depth of soil, depending on the soil bulk density. If you do not know your soil<br />
bulk density, 3.6 is a good starting place. See the conversion tools for details.<br />
If soil test is in ppm, convert:<br />
ppm x 3.6 =<br />
NO3-N soil bulk density<br />
lb. N/A<br />
NO3-N<br />
JCS-<strong>Organic</strong> Grower_1Q<strong>2021</strong>_<strong>April</strong> Print Ad_Final.pdf 1 3/15/21 5:49 PM<br />
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<strong>April</strong>/<strong>May</strong> <strong>2021</strong> www.organicfarmermag.com 9
Understanding the<br />
Economics of <strong>Organic</strong><br />
Seed Production<br />
By KIKI HUBBARD | <strong>Organic</strong> Seed Alliance<br />
<strong>Organic</strong> seed production can be an economic opportunity for organic growers (photo by Broken Banjo Photography.)<br />
<strong>Organic</strong> seed production is a<br />
developing industry and viable<br />
economic opportunity for organic<br />
growers. To help growers manage the<br />
uncertainties and risks inherent to seed<br />
production, and to help growers earn<br />
more profit, <strong>Organic</strong> Seed Alliance<br />
(OSA) recently published an online<br />
toolkit to assist organic seed growers<br />
and seed enterprises. The toolkit serves<br />
as the first of its kind to focus on organic<br />
seed production specifically, offering<br />
support in the form of budgeting<br />
spreadsheets, inventory management,<br />
and foundation and stock seed planning.<br />
Seed production can be deeply rewarding<br />
work. However, turning a passion<br />
for seeds into a viable livelihood is a<br />
challenge that even experienced seed<br />
growers struggle to overcome. That’s<br />
why this entire toolkit was developed in<br />
partnership with agricultural economists<br />
at Highland Economics— experienced<br />
professionals who understand<br />
the importance of a farm budget and<br />
production plan.<br />
Tracking Expenses and Budgets<br />
The first tool in the Seed Economics<br />
Toolkit is a spreadsheet that helps growers<br />
track the costs associated with producing<br />
seed crops. Enterprise budgets<br />
provide a snapshot of costs associated<br />
with a crop for a single year and do not<br />
make predictions or forecasts for future<br />
years. However, they can be used to<br />
provide guidance for growers who are<br />
considering investments in new equipment<br />
and scaling up.<br />
Stock and Foundation<br />
Seed Production<br />
Common questions around foundation,<br />
stock and production seed include:<br />
How much foundation seed do I need<br />
to ensure I have enough stock seed?<br />
How much stock seed should I produce<br />
every third year for my production<br />
seed? This second spreadsheet helps<br />
guide decisions around how much and<br />
how often to produce foundation, stock,<br />
and production seed based on your<br />
operation, desired inventory, longevity<br />
of the seed and estimated yield.<br />
Tracking Labor<br />
Tracking on-farm labor can be confusing<br />
and overwhelming, but it is also<br />
extremely important for growers trying<br />
to get a handle on their operation costs.<br />
A third piece of this toolkit is designed<br />
as a guide for tracking your operation<br />
each day, including a form designed<br />
for routine activities over the course of<br />
many days (such as watering in a greenhouse<br />
or screening a large seed lot) for<br />
tracking labor in seed production.<br />
Getting Seed Contracts<br />
Success in seed production contracts<br />
requires careful management of the<br />
grower-buyer relationship and an<br />
understanding of the terms of the contract.<br />
Learning from others’ experience<br />
can save many headaches and ensure<br />
a successful grower-buyer relationship.<br />
Over the years, experienced seed<br />
growers and buyers have shared their<br />
experiences and advice in workshops<br />
and webinars at the <strong>Organic</strong> Seed<br />
Growers Conference and other online<br />
networking events. Several of these<br />
webinars also offer contact information<br />
Continued on Page 12<br />
10 <strong>Organic</strong> <strong>Farmer</strong> <strong>April</strong>/<strong>May</strong> <strong>2021</strong>
®<br />
IMAGINATION<br />
INNOVATION<br />
SCIENCE IN ACTION
Continued from Page 10<br />
and guidance on how to reach out to<br />
seed companies when seeking contracts<br />
(all of these webinars are provided as<br />
part of the Seed Economics Toolkit at<br />
the link at the end of the article.)<br />
The best time to contact seed companies to<br />
inquire about contract opportunities is between<br />
September and January when companies are<br />
‘preparing for the following year’s production.<br />
Growing seed on contract for a seed<br />
company takes some of the sales-related<br />
risks out of seed production, but<br />
finding the opportunity to grow on<br />
contract can also be a hurdle as it is not<br />
always clear how to connect with a seed<br />
company to acquire contracts. Seed<br />
companies and growers alike report<br />
that they most often make new relationships<br />
by networking at conferences,<br />
such as the <strong>Organic</strong> Seed Growers<br />
Conference, and other regional events.<br />
Many seed growers also cold call<br />
companies to see if they’re looking to<br />
contract with new growers.<br />
As an organization that strives to create<br />
networking opportunities for seed<br />
growers, OSA developed an online registry<br />
called the <strong>Organic</strong> Seed Producers<br />
Directory to connect seed growers with<br />
seed companies. It includes a user profile<br />
that shares each grower’s location,<br />
scale and crop expertise. In this way,<br />
the directory can be searched by seed<br />
companies seeking new growers and for<br />
producers to connect with one another<br />
as well.<br />
If you are an organic seed grower who<br />
would like to join this directory, create<br />
a profile today to start connecting with<br />
seed companies and other growers at:<br />
seedalliance.org/directory/.<br />
Seed Company Advice<br />
Prices for wholesale production vary<br />
widely by crop, variety and scale as<br />
well as terms of the contract. The roles<br />
and expectations of the producer also<br />
influence the pricing in a production<br />
contract and understanding the expectations<br />
of the seed company is very<br />
important as it significantly influences<br />
the risks and costs of production.<br />
While prices vary widely from company<br />
to company and depend on a multitude<br />
of factors, it is also helpful to have<br />
some ballpark idea of average wholesale<br />
prices to help in negotiating contracts<br />
and using the enterprise budgeting tool<br />
to project profit potential.<br />
OSA surveyed nine seed companies to<br />
solicit feedback on best practices for<br />
engaging in contract seed production<br />
and to inquire about average contract<br />
prices for specific crops to help growers<br />
develop production plans (these prices<br />
are listed in the online toolkit at the<br />
link at the end of the article.) Contract<br />
prices often varied widely between<br />
companies and within a given crop<br />
by each company. Commonly mentioned<br />
determinants of prices included<br />
production scale; variety type (high or<br />
low yielding, ease of production); roles<br />
of producer, such as need for rogueing<br />
or finished quality seed cleaning; seed<br />
quality, such as germination rate and<br />
disease testing; and whether the crop is<br />
an open-pollinated or hybrid variety.<br />
Below is a summary of best practices<br />
shared by seed companies:<br />
The best time to contact seed companies<br />
to inquire about contract opportunities<br />
is between September and<br />
January when companies are preparing<br />
for the following year’s production.<br />
Communication is critical to maintaining<br />
a good contract relationship. Most<br />
companies request an update on the<br />
crop status two to three times throughout<br />
the growing season. Photos of the<br />
crop and updates on any off types are<br />
very helpful.<br />
Timely delivery of clean seed is important<br />
as it helps the company prepare for<br />
the following year’s sales.<br />
If you are new to contract production,<br />
start small and try crops that you are<br />
familiar with growing. Try a test plot<br />
the first year if it is a new crop you are<br />
unfamiliar with so you can determine<br />
if you can grow it in your location. Also,<br />
plan for how you will harvest and handle<br />
the finished seed crop.<br />
Keep good records on your costs of<br />
production, including your time, so<br />
that you are able to engage in informed<br />
negotiations on price.<br />
Share your production information<br />
with the company and ask them to<br />
share what they know about the crop.<br />
Seed companies want to learn from<br />
your experience and also help you<br />
succeed. It takes an open exchange of<br />
information to ensure everyone’s success.<br />
If you need help, ask!<br />
To access the Seed Economics Toolkit,<br />
visit seedalliance.org/publications/<br />
seed-economics-toolkit/.<br />
Comments about this article? We want<br />
to hear from you. Feel free to email us at<br />
article@jcsmarketinginc.com<br />
’<br />
12 <strong>Organic</strong> <strong>Farmer</strong> <strong>April</strong>/<strong>May</strong> <strong>2021</strong>
Strawberries in <strong>May</strong> (peak production period for San Luis Obispo) of non-solarized (left) and solarized plots (right) (all photos courtesy A.M. Tubeileh.)<br />
Biosolarization and<br />
Cover Crop Impact on<br />
Weeds and Soilborne<br />
Pathogens<br />
By TIMOTHY JACOBS | Risk Management Specialist, USDA<br />
and ASHRAF M. TUBEILEH | Cal Poly, San Luis Obispo<br />
Soils contain a lot of good things, but they are also<br />
reservoirs for weeds, pathogens and nematodes, which,<br />
if left uncontrolled, can devastate crop yields. If soilborne<br />
pests rise to economically damaging levels, it becomes<br />
necessary for growers to use soil disinfestation techniques to<br />
kill soilborne organisms.<br />
Most conventional growers use fumigants for soil disinfestation.<br />
Fumigation is unavailable to organic growers leaving<br />
organic growers few options for controlling soilborne<br />
pests. However, over the past couple of decades, there has<br />
been substantial research into organic soil disinfestation<br />
techniques due to increasing regulations for conventional<br />
fumigants. Researchers at California Polytechnic State University,<br />
San Luis Obispo recently conducted research on soil<br />
solarization and biosolarization, two organic soil disinfestation<br />
techniques, on organic strawberry production at the<br />
Cal Poly <strong>Organic</strong> Farm in San Luis Obispo, Calif.<br />
Strawberry beds undergoing solarization during August.<br />
Soil Solarization<br />
Solarization involves placing clear, thin (25 to 50μm),<br />
low-density polyethylene tarps over irrigated soil to increase<br />
soil temperatures to lethal levels for pathogens, pests and<br />
weeds. In general, temperatures generated during soil solarization<br />
range from 104 to 158 degrees F. The tarp is left on<br />
the soil for four to eight weeks, depending on the soil temperatures<br />
generated during solarization. The efficacy of solarization<br />
is primarily based on ambient air/soil temperatures<br />
and intensity of solar radiation. In most cases, solarization<br />
should raise the ambient soil temperature between 10 and 20<br />
degrees C (18 to 36 degrees F) in the top six inches of the soil.<br />
14 <strong>Organic</strong> <strong>Farmer</strong> <strong>April</strong>/<strong>May</strong> <strong>2021</strong>
Germination (% )<br />
100<br />
90<br />
80<br />
70<br />
60<br />
50<br />
40<br />
30<br />
20<br />
10<br />
species<br />
annual sowthistle<br />
bristly oxtongue<br />
common lambsquarters<br />
common purslane<br />
little mallow<br />
pigweed<br />
0<br />
0 40 80 120 160 200 240 280 320<br />
Hours<br />
Figure 1. Logistic regression models showing how germination rate of different weed species is affected by the duration of exposure to 122<br />
degrees F under laboratory conditions simulating solarization.<br />
Solarization is most effective when used during the summer<br />
when solar radiation is high in sunny, warm climates. Costs<br />
of solarization vary depending on plastic prices, but in general,<br />
the plastic costs in between $150 to $300 per acre. The<br />
best plastics are clear/transparent, one to three millimeters<br />
thick and UV-inhibited to prevent breakdown in sunlight.<br />
Biosolarization, which combines the use of organic soil<br />
amendments and soil solarization, has been proven to<br />
enhance the results of solarization in numerous field experiments.<br />
<strong>Organic</strong> amendments commonly used are plant<br />
residues, animal manure, compost and other high-nitrogen<br />
organic materials such as blood meal. Biosolarization is a relatively<br />
new area of research and can reduce the time needed<br />
for solarization as well as increase solarization’s effectiveness<br />
in areas with marginal conditions for solarization. For<br />
example, in San Luis Obispo, we are about five miles from<br />
the coast, experience frequent, foggy mornings and rarely<br />
have temperatures above 90 degrees F. We included biosolarization<br />
of cover crop residues in our experiment to see if it<br />
would increase the efficacy of solarization in our climate.<br />
The rest of this article will focus on the results from our<br />
research. For more information on solarization and biosolarization,<br />
including application techniques, please see our<br />
previous <strong>Organic</strong> <strong>Farmer</strong> article from <strong>April</strong>/<strong>May</strong> 2019 or UC<br />
extension’s webpage on solarization ipm.ucanr.edu/PMG/<br />
PESTNOTES/pn74145.html.<br />
Solarization Research<br />
As part of our research, we conducted lab experiments under<br />
simulated solarization conditions assessing the time needed<br />
to kill weed seeds at five different temperatures (104, 113, 122,<br />
131 and 140 degrees F). Seeds tested included little mallow,<br />
redstem filaree, bristly oxtongue, annual sow thistle, common<br />
purslane, common lambsquarters and redroot pigweed.<br />
Efficacy of solarization temperatures differed between<br />
different species. In general, cool-season annuals annual<br />
sow thistle and bristly oxtongue were more susceptible to<br />
heat treatments than warm-season annuals such as redroot<br />
pigweed. Additionally, hard seeded (thick seed coats) seed<br />
were relatively unaffected by heat treatments taking long<br />
duration to kill. Time and percent mortality of weed seeds<br />
were used to create thermal death models for weed seeds<br />
at each temperature (Figure 1). Additionally, models were<br />
Continued on Page 16<br />
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<strong>April</strong>/<strong>May</strong> <strong>2021</strong> www.organicfarmermag.com 15
• fdf<br />
Continued from Page 15<br />
used to estimate the amount of time<br />
needed to kill 90% of seeds for all species<br />
tested (Figure 2). Redstem filaree<br />
germination rates were unaffected by<br />
heat treatments. Additionally, common<br />
purslane was unaffected by heat<br />
treatments below 113 degrees F or lower<br />
and redroot pigweed was unaffected by<br />
temperatures of 104 degrees F or below.<br />
Results indicated daily temperatures<br />
above 122 degrees F are needed for<br />
four to eight weeks to achieve adequate<br />
weed management via solarization.<br />
Time (hours)<br />
700<br />
600<br />
500<br />
400<br />
300<br />
200<br />
100<br />
0<br />
Time needed to achieve 90% mortality<br />
45° C<br />
50° C<br />
55° C<br />
40° C<br />
40° C<br />
45° C<br />
50° C<br />
55° C<br />
50° C<br />
Little mallow<br />
Bristly<br />
oxtongue<br />
55° C<br />
60° C<br />
Common<br />
purslane<br />
40° C<br />
45° C<br />
50° C<br />
55° C<br />
60° C<br />
Common<br />
lambsquarters<br />
45° C<br />
50° C<br />
55° C<br />
Redroot<br />
pigweed<br />
60° C<br />
40° C<br />
45° C<br />
50° C<br />
55° C<br />
Annual<br />
sowthistle<br />
We also conducted field experiments on<br />
solarization of sudangrass residues in<br />
organic strawberry production.<br />
The objectives of our field experiment<br />
were:<br />
Species<br />
Figure 2. Time needed to reduce germination rates by 90% for six different species at<br />
five different temperatures (40°C=104°F, 45°C=113°F, 50°C =122°F, 55°C=131°F, 60°C=140°F )<br />
according to logistic regression models.<br />
• To determine if soil solarization<br />
can reduce weed and pathogen<br />
pressures and improve plant health<br />
and strawberry yields in San Luis<br />
Obispo County,<br />
• To determine if the effect of sudangrass<br />
cover crop residues will<br />
increase the effects of soil solarization,<br />
and<br />
• To compare the effects of sudangrass<br />
residue mulching vs. incorporation<br />
on weed populations, pathogen<br />
populations and strawberry health<br />
and yields.<br />
The experiment was designed so that<br />
we had three cover crop treatments:<br />
A control, one where sudangrass was<br />
left as a surface mulch after mowing,<br />
and the other where sudangrass was<br />
incorporated into the soil after mowing.<br />
Within each cover crop treatment, we<br />
solarized half and left the other half<br />
non-solarized.<br />
‘Piper’ sudangrass was planted in mid-<br />
<strong>May</strong> using a seed drill. In mid-July,<br />
sudangrass was chopped and shredded<br />
with a tractor-drawn flail mower and<br />
incorporated into the soil in our incorporated<br />
treatment. After incorporation,<br />
beds were created in all plots except<br />
mulched plots. In mulched treatments,<br />
sudangrass residue was left on the<br />
soil surface and no beds were created.<br />
On July 26, solarization plastic was<br />
hand-applied onto solarized plots. After<br />
applying plastic, fields were irrigated<br />
for 72 hours using one line of drip tape<br />
till fields reached field capacity. Tarps<br />
were left on for five weeks and removed<br />
on August 31, 2018. Strawberries were<br />
planted in October after doing weed<br />
population assessments in our various<br />
treatments.<br />
Results<br />
Maximum soil temperatures in solarized<br />
plots were 118 degrees F at a soil<br />
depth of two inches and 42 degrees C<br />
at a soil depth of 6 inches. On average,<br />
temperatures in cover crop mulched<br />
plots were 4 to 6 degrees F lower than<br />
other solarized plots. Temperatures in<br />
all solarized plots were 18 to 30 degrees<br />
F higher than non-solarized plots. In<br />
initial weed biomass assessments taken<br />
six weeks after tarp removal, non-solarized<br />
incorporated plots reduced weed<br />
biomass by 24.4% compared to the<br />
control. Non-solarized mulched plots<br />
reduced weed biomass by 95.6% compared<br />
to the control. All solarized plots<br />
resulted in similar reduction in weed<br />
biomass compared to the control with<br />
an average reduction of 97.1% ± 0.6%.<br />
Efficacy of solarization treatments<br />
decreased with time. In final weed<br />
biomass assessments taken 15 weeks<br />
after tarp removal, the only solarization<br />
treatment providing a significant<br />
reduction in weed biomass compared<br />
to the control was incorporated plots<br />
with solarization resulting in 67% lower<br />
biomass than the control. Mulched<br />
plots without solarization also provided<br />
significant control, reducing weed biomass<br />
to 84.1% of the control. However,<br />
in non-solarized mulched treatments,<br />
the sudangrass re-grew after mowing<br />
and did not die until the winter.<br />
Continued on Page 18<br />
16 <strong>Organic</strong> <strong>Farmer</strong> <strong>April</strong>/<strong>May</strong> <strong>2021</strong>
<strong>April</strong>/<strong>May</strong> <strong>2021</strong> www.organicfarmermag.com 17
Non-solarized (left) and solarized (right) beds of strawberries during June.<br />
Sudangrass Effect<br />
Mulched<br />
Incorporated<br />
None<br />
Yields per 30<br />
plants (g)<br />
8820 a<br />
7501 a<br />
6480 a<br />
Solarization effect<br />
Solarized<br />
Non-Solarized<br />
Yields per 30<br />
plants (g)<br />
11,595 a<br />
3,609 b<br />
Table 1. The yield in grams per 30 plants from solarized treatments (n=12) and sudangrass<br />
treatments (n=8) from March through June.<br />
Continued from Page 16<br />
the effect of solarization. Cover crop<br />
treatments did not have a significant<br />
effect on verticillium populations or<br />
yields. Mulched treatments did reduce<br />
weed population and had lower disease<br />
severity than other treatments.<br />
Solarization effectively killed mowed<br />
sudangrass, preventing it from regrowing.<br />
Solarization of mowed cover crops<br />
provides a potential mechanism for<br />
killing cover crops for organic growers<br />
wishing to perform no-till production.<br />
However, more research is needed into<br />
this topic.<br />
This led to poor strawberry establishment,<br />
although the strawberries later<br />
recovered.<br />
plant mortality was significantly higher<br />
in non-solarized plots with 35.5%<br />
mortality compared to 16.0 % mortality<br />
in solarized plots. Additionally, solarized<br />
plots had much higher yield than<br />
non-solarized plots. The different cover<br />
crop treatments did not have a clear<br />
effect on reducing verticillium wilt<br />
population, disease severity or increasing<br />
yields.<br />
The effectiveness of solarization depends<br />
not only on the temperatures<br />
you can achieve, but on the disease<br />
and weed species present in a field as<br />
well. Particularly in areas with cooler<br />
climates or frequent foggy/cloudy<br />
days during the summer, knowing the<br />
temperature thresholds required to kill<br />
the pests in your field can be important<br />
in determining whether solarization<br />
is a viable solution. This is another<br />
area where more research can be done.<br />
First, develop models to help growers<br />
estimate the temperatures they can<br />
achieve during solarization. Secondly,<br />
Solarization reduced verticillium wilt<br />
populations by 80.7% compared to<br />
non-solarized plots. Solarized plots had<br />
much lower disease incidence throughout<br />
the growing season. Non-solarized<br />
plots started to experience disease<br />
symptoms in <strong>April</strong> and were not producing<br />
fruit by <strong>May</strong>. Solarized plots<br />
experienced almost no disease pressure<br />
till late <strong>May</strong>/June when temperatures<br />
warmed. Solarized plants experienced<br />
disease pressure from Charcoal Rot,<br />
Macrophomina phaesolina, a warm-sea-<br />
Key Takeaways<br />
Solarization provided effective weed<br />
Biosolarization and<br />
management for 3.5 months after tarp<br />
removal, reduced verticillium wilt populations,<br />
reduced<br />
models can be used to determine the<br />
Cover Crop<br />
disease severity<br />
Impact<br />
and susceptibility of different<br />
on<br />
pest species to<br />
increased yield compared to non-solarized<br />
plots.<br />
Comments about this article? We want<br />
solarization.<br />
son pathogen which we theorize was<br />
not reduced to the same degree<br />
Weeds<br />
as verticillium<br />
wilt populations were. Total Cover crop treatments did not enhance article@jcsmarketinginc.com<br />
and Soilborne<br />
to hear from you. Feel free to email us at<br />
Pathogens<br />
18 <strong>Organic</strong> <strong>Farmer</strong> <strong>April</strong>/<strong>May</strong> <strong>2021</strong>
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USDA Passes Final Rules<br />
on Hemp Growing<br />
Agency Makes Changes Based on Grower<br />
Input and Experiences<br />
By DANITA CAHILL | Contributing Writer<br />
Open-pollinated field of hemp plants in Nicolaus, Calif. (all photos courtesy J. Eve.)<br />
Hemp flowers.<br />
Just when you thought you knew<br />
all the rules and laws that regulated<br />
legal hemp growing in the U.S.<br />
at the federal level, the United States<br />
Department of Agriculture (USDA)<br />
went and made changes to those rules.<br />
They didn’t do it to cause headaches, but<br />
rather because they listened to what<br />
the public had to say and what growers<br />
learned during the 2020 growing season.<br />
The regulations that first came out after<br />
the 2018 Farm Bill passed into law was<br />
Justin Eve believes rules for hemp are being rushed.<br />
an interim final rule. The interim regulations<br />
were published on October 31,<br />
2019 and laid out guidelines for hemp<br />
growers to legally register, test their<br />
plants to stay within the THC limitations<br />
and generally stay out of trouble<br />
with the law.<br />
On January 15, <strong>2021</strong>, the USDA published<br />
a final rule. Those updated hemp<br />
regulations took effect on March 22,<br />
<strong>2021</strong>. Below is a general overview of the<br />
final federal regulations.<br />
Since the law<br />
may vary from state<br />
to state and within<br />
tribal land, be sure to<br />
check the regulations<br />
within your own state<br />
or jurisdiction.<br />
Violation for Too<br />
Much THC<br />
As was law before,<br />
plants that test too<br />
high in tetrahydrocannabinol<br />
(THC), a<br />
cannabinoid, must be<br />
destroyed. The final<br />
rule raises the amount<br />
from 0.5% to 1%. If<br />
plants test at or below<br />
the 1% threshold, there<br />
is no “negligent violation.”<br />
A grower can<br />
only receive one such<br />
violation in any given growing season.<br />
Scientists estimate there are more than<br />
100 different cannabinoids in hemp.<br />
More studies are currently underway.<br />
Of those cannabinoids, two are the<br />
most well-known. The first is THC.<br />
It’s the hallucinogenic, or recreational<br />
component in cannabis (marijuana).<br />
THC is also found in hemp, but generally<br />
in much smaller amounts. The<br />
second most recognized is Cannabidiol<br />
(CBD), the popular medical cannabinoid<br />
in hemp. CBD is also found in<br />
cannabis.<br />
Plants over the 1% THC threshold can<br />
be destroyed in more ways than before.<br />
No longer will a grower be required to<br />
use only law enforcement or a Drug<br />
Enforcement Administration (DEA)<br />
reverse distributor, which is a person<br />
or company that reclaims outdated or<br />
otherwise unusable drugs and destroys<br />
them. Reverse distributors are registered<br />
with the DEA.<br />
According to reports submitted by<br />
states and tribes in 2020, growers planted<br />
6,166 acres under the 2018 Farm<br />
Bill hemp plans and about 730 acres of<br />
those had to be destroyed for noncompliance.<br />
Plant Testing<br />
Since there aren’t enough labs regis-<br />
20 <strong>Organic</strong> <strong>Farmer</strong> <strong>April</strong>/<strong>May</strong> <strong>2021</strong>
Strengthen cell<br />
walls and lessen<br />
the impact of<br />
abiotic stress.<br />
A 2019 midwestern hemp crop.<br />
tered with the DEA for the amount of<br />
hemp production expected in <strong>2021</strong>, the<br />
DEA is allowing non-DEA registered<br />
labs to test hemp. This is an extension<br />
only until January 1, 2022. In the<br />
meantime, the DEA is trying to quickly<br />
process lab applications to get more<br />
testing labs registered.<br />
The timing of plant sample collection<br />
has been extended. The interim regulations<br />
gave only a 15-day window from<br />
testing to harvest. That time frame has<br />
been raised to 30 days.<br />
Growers asked for a change in the<br />
sampling method. They requested that<br />
larger samples be taken from each plant<br />
sampled, or that the whole plant be<br />
sampled. They also asked that samples<br />
be taken from fewer plants.<br />
The final regulations let individual<br />
states and tribes set their own policies<br />
using a performance-based approach to<br />
sampling. These policies must be written<br />
into a plan and sent to the USDA<br />
for approval. The plan may consider the<br />
state’s seed certification programs, the<br />
history of grower compliance and other<br />
factors as determined by tribe or state.<br />
Tribal Regulations<br />
The rules were a little fuzzy about tribal<br />
jurisdiction in the interim regulations.<br />
Those initial rules didn’t specifically<br />
discuss if a tribe with an approved<br />
USDA plan had primary rule of law<br />
over hemp production across its entire<br />
territory, or only over land in which it<br />
had inherent jurisdiction.<br />
Since tribes rule themselves as quasi-sovereign<br />
nations, the USDA decided<br />
in the final regulations that a tribe may<br />
exercise jurisdiction, and therefore regulatory<br />
authority, over hemp production<br />
in all of its territory no matter the<br />
extent of the tribe’s inherent regulatory<br />
authority (generally, tribes can’t exercise<br />
criminal or civil jurisdiction over<br />
non-tribe members.)<br />
A Hemp Researcher’s Perspective<br />
So how do hemp researchers and growers<br />
feel about the hemp final regulations?<br />
And how do these regulations<br />
affect them?<br />
“Working with hemp as a researcher<br />
poses unique challenges because of the<br />
regulatory factor,” said Sarah Light,<br />
UCCE agronomy advisor in Sutter,<br />
Yuba and Colusa Counties. “It’s just the<br />
nature of working with the crop.”<br />
Light sees the final rule as a positive<br />
rather than a negative. “Now that we<br />
have the final ruling, we can move<br />
ahead. Now we know,” she said. “We’re<br />
Continued on Page 22<br />
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208-678-2610<br />
<strong>April</strong>/<strong>May</strong> <strong>2021</strong> www.organicfarmermag.com 21
An indoor canopy of hemp plants.<br />
In addition to hemp, Eve also grows moringa and sweet potatoes<br />
on 20 acres north of Sacramento, Cal. His background<br />
is in bioenergy, plant sciences and soil chemistry. He sees a<br />
high level of importance in getting viable hemp genetics that<br />
hemp farmers can grow, harvest and make some money on<br />
while staying within the legal boundaries of the regulations.<br />
Hemp growers like Eve are banding together to form the<br />
Hemp <strong>Farmer</strong>s Guild. The guild is working with the DEA<br />
and the USDA to help them understand the growing challenges<br />
of hemp from a farmer’s perspective.<br />
So, are the federal agencies listening to hemp growers?<br />
“They are,” Eve said, but added a caveat about the USDA,<br />
“They’re not really farmers. They’re not granting us a buffer to<br />
make some mistakes as we go along.”<br />
Justin Eve stands next to one of his hemp plants<br />
Continued from Page 21<br />
excited to keep doing research for our growers. We’ll just<br />
continue to be in compliance.”<br />
A Hemp Grower’s Perspective<br />
Justin Eve, owner of 7 Generations Producers, is a USDA-certified<br />
organic grower. He has a different take on the regulations.<br />
“They’re classifying it and approaching it like some sort of<br />
drug,” he said. “It’s a little upsetting to me.<br />
This is an agricultural crop. We already have those regulations<br />
in place. We don’t need to recreate the wheel.”<br />
Eve is frustrated with how the USDA and the DEA focus<br />
on THC levels within hemp. “It’s such a miniscule aspect to<br />
what this crop can be,” he said. “America made its way with<br />
hemp.” (The early drafts of the Declaration of Independence<br />
and the Bill of Rights were written on hemp paper).<br />
The way the regulations are written makes Eve believe there’s<br />
not a lot of wiggle room. “It’s limiting a farmer to harvesting<br />
within 30 days. It’s unconstitutional. We just want to grow<br />
a good crop and not get arrested for what we thought was<br />
legal. “The limitation on THC is low. The way they’re testing<br />
is skewed,” Eve said. If the plants test too high in THC, they<br />
must be destroyed; there’s no other path. Eve mentioned a<br />
hemp grower in the Merced area that had to destroy a 200-<br />
acre, $2 million crop. “It can bankrupt farmers.”<br />
Big companies are hesitant to get involved with the business,<br />
according to Eve. But for the industry to flourish, it will take<br />
large companies investing in expensive processing facilities.<br />
“The major companies are afraid of backlash from the USDA,<br />
the FDA and the DEA,” Eve said.<br />
As for the timing of the final rule, Eve thinks it was rushed.<br />
“We should have two more years to figure out a final rule,” he<br />
said. He believes that state departments and local ag departments<br />
don’t fully understand the USDA regulations. “The<br />
head doesn’t know what the tail is doing.<br />
“I think the USDA is heading in the right direction, but up to<br />
this point, it’s been too hard,” Eve said.<br />
Comments about this article? We want to hear from you.<br />
Feel free to email us at article@jcsmarketinginc.com<br />
22 <strong>Organic</strong> <strong>Farmer</strong> <strong>April</strong>/<strong>May</strong> <strong>2021</strong>
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Research into<br />
Alfalfa Crop<br />
Rotation for<br />
<strong>Organic</strong><br />
Tomatoes<br />
By SABRINA HALVORSON | Contributing Writer<br />
The practice of rotating alfalfa<br />
with tomatoes was once more<br />
popular than it is today, but recent<br />
research suggests it offers soil health<br />
benefits in organic tomato crops.<br />
Researchers Nicole Tautges, Emily<br />
Woodward and Dan Putnam tested a<br />
three-year rotation of tomatoes, corn<br />
and alfalfa at the UC Davis Russell<br />
Ranch Sustainable Agriculture Facility.<br />
According to their research, alfalfa benefited<br />
tomato yields when in rotation,<br />
with fruit yields between 10% to 26%<br />
greater following three-year alfalfa as<br />
compared to following corn in a twoyear<br />
tomato-corn rotation.<br />
anecdotal or observational<br />
evidence<br />
that growers reported<br />
seeing on the ground<br />
in their crop rotation,”<br />
said Tautges,<br />
now a researcher<br />
with Michael Fields<br />
Agricultural Institute<br />
in East Troy, Wisc. “A<br />
lot of growers would say that they have<br />
better soil health and the soil was more<br />
workable following alfalfa compared to<br />
following other annual crops. They’re<br />
seeing yield boosts. They’re seeing<br />
decreases in disease and pathogen pressure<br />
in the following vegetable crop.”<br />
Alfalfa grows on test plots at the UC Davis Russell Ranch Sustainable<br />
Agriculture Facility. Researchers tested the use of alfalfa in crop rotations<br />
versus corn when growing organic tomatoes (photo<br />
courtesy N. Tautges.)<br />
at the end of each rotation crop with<br />
the objective of seeing how the differences<br />
persisted in time throughout the<br />
rotation. They planted tomatoes after<br />
both crops and measured the same<br />
indicators in the tomatoes to see how<br />
they compared to the findings from the<br />
previous crop.<br />
“This research was motivated by a lot of<br />
"<br />
“There was a real<br />
visual difference<br />
in the vine health<br />
among the systems,<br />
and I think that<br />
contributed to the<br />
stronger yields also."<br />
− Nicole Tautges, UC Davis<br />
Tautges said there has been limited research<br />
into forages and what exactly the<br />
biological and chemical mechanisms<br />
were that were driving those comments<br />
from growers.<br />
“It’s all qualitative at this point. So, I<br />
wanted to take a stab at doing that<br />
research,” she said.<br />
Tautges explained they measured a<br />
suite of soil health indicators – biological,<br />
chemical and physical – in<br />
the soil at the end of the alfalfa crop<br />
compared to the corn as their annual<br />
control. They compared the indicators<br />
In addition to monitoring the various<br />
indicators in the soil, they kept track of<br />
yields from the tomato crops and found<br />
an increase in tomatoes that followed<br />
alfalfa.<br />
“We saw about a 3- to 5-ton-per-acre<br />
increase in tomato fruit yields. At times,<br />
we did see even up to 10 tons per acre,”<br />
she said. She said while there were<br />
some individual cases of higher yields,<br />
the increase was generally around 10%<br />
minimum.<br />
She said they also noticed some other<br />
results visually. The plants were greener,<br />
24 <strong>Organic</strong> <strong>Farmer</strong> <strong>April</strong>/<strong>May</strong> <strong>2021</strong>
ushier and bigger. “There was a real<br />
visual difference in the vine health<br />
among the systems, and I think that<br />
contributed to the stronger yields also.”<br />
Their research findings broke down<br />
findings in terms of soil health. The<br />
research showed alfalfa enhanced soil<br />
microbial biomarkers and the nitrogen<br />
uptake of the soil microbial pool after<br />
three years compared to the corn. The<br />
alfalfa also showed higher levels of<br />
mycorrhizal fungi in the soil. The mycorrhizal<br />
fungi biomarkers were 45%<br />
higher in alfalfa soil than in corn soil.<br />
There were differences in nutrients as<br />
well. The research states total dissolved<br />
nitrogen in the soil solution was more<br />
than two times greater following corn<br />
than following alfalfa. That dissolved<br />
nitrogen represents a pool of potentially<br />
leachable nitrogen, the research<br />
explains. It also states greater potentially<br />
leachable nitrate in the fall lead<br />
to greater measured nitrate leaching<br />
losses over the winter. According to the<br />
research, nitrate leached with winter<br />
precipitation was lower following alfalfa<br />
compared to conventional corn.<br />
When it comes to nitrogen, Tautges said<br />
things get more complicated.<br />
“There should be nitrogen going into<br />
the microbial community and there<br />
should be nitrogen going into the soil<br />
by all of the organic matter decomposition<br />
that we’re getting from the alfalfa,”<br />
she explained.<br />
Another result from the alfalfa rotation<br />
is a change in soil structure. The<br />
researched showed alfalfa greatly improved<br />
soil aggregation, which Tautges<br />
said is an important indicator of soil<br />
structure.<br />
“We had hypothesized that alfalfa having<br />
a deeper, bigger root system would<br />
be punching more holes in the soil and<br />
aerating the soil more. Fungi that were<br />
being maintained better in the alfalfa<br />
system would be leading to better soil<br />
aggregation through the compounds<br />
fungi secrete,” she explained.<br />
While those factors were leading to<br />
improved soil aggregation, one factor<br />
of growing alfalfa was having a counter<br />
effect. “The haying activities also were<br />
increasing bulk density because you’re<br />
driving equipment across the field a lot<br />
without using any tillage to break it up<br />
again.”<br />
The research did find a couple of issues<br />
with the alfalfa rotation. Findings<br />
indicated the alfalfa tended to deplete<br />
soil cations, which left low levels of<br />
potassium and calcium fertility for<br />
the following tomato crop. However,<br />
overall, researchers determined alfalfa<br />
benefits biological and physical soil<br />
health parameters and tightens nitrogen<br />
cycling.<br />
Comments about this article? We want<br />
to hear from you. Feel free to email us at<br />
article@jcsmarketinginc.com<br />
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<strong>April</strong>/<strong>May</strong> <strong>2021</strong> www.organicfarmermag.com 25
Food Safety Laws and<br />
Standard Operating<br />
Procedures for<br />
Urban <strong>Farmer</strong>s<br />
By TAYLOR CHALSTROM | Assistant Editor<br />
Youth farmers at WOW urban farm in Oakland. Urban farming continues to rise in<br />
popularity as a way for urban communities to tackle food insecurity and promote food<br />
sovereignty (all photos by R. Surls.)<br />
26 <strong>Organic</strong> <strong>Farmer</strong> <strong>April</strong>/<strong>May</strong> <strong>2021</strong>
As urban farming continues to rise in<br />
popularity as a way for urban communities<br />
to tackle food insecurity and promote<br />
food sovereignty, new laws and standard<br />
operation procedures are being put into place<br />
to ensure food safety of those products. The<br />
California Urban Agriculture Food Safety<br />
Guide, produced in December 2020 by UC<br />
Berkeley, UCCE and Sustainable Economies<br />
Law Center, provides a thorough overview of<br />
what those urban farmers or gardeners may<br />
be subject to.<br />
“For new urban farmers, it outlines relatively<br />
new laws that offer new opportunities for<br />
urban farmers and gardeners to grow and<br />
distribute foods for sale including the Cottage<br />
Food Act and the Community Food Producer<br />
Act,” said Jennifer Sowerwine, UCCE metropolitan<br />
agriculture and food safety specialist<br />
at UC Berkeley and lead author of the guide.<br />
“We tried to take complex regulations and put<br />
them into a format that will be more accessible<br />
for very small-scale growers,” added<br />
Rachel Surls, UCCE sustainable food systems<br />
advisor and co-author.<br />
Radishes for sale at an urban farm<br />
in Ontario, Calif. The 72-page guide<br />
clarifies that all food grown and sold<br />
or donated in urban environments<br />
should be following the CDFA’s Small<br />
Farm Food Safety Guidelines.<br />
Handwashing station<br />
at an urban farm in San<br />
Diego. CDFA’s Small Farm<br />
Food Safety Guidelines<br />
dictate that proper hygiene<br />
should be followed<br />
in every step of the<br />
growing process.<br />
Surls noted that products produced and distributed by<br />
urban farmers have long existed in a “legal gray area” and<br />
that new laws like the ones outlined in the guide are clearing<br />
things up.<br />
Continued on Page 28<br />
The 72-page guide also explains whether or<br />
not urban farmers may be subject to the Food<br />
Safety Modernization Act (FSMA), and clarifies<br />
that all food grown and sold or donated<br />
in urban environments should be following<br />
the CDFA’s Small Farm Food Safety Guidelines,<br />
according to Sowerwine.<br />
DON’T FORGET THE SEASOL...<br />
Solutions for the Earth<br />
“Generally, any farm or organization in<br />
California that grows or distributes produce<br />
offered for public consumption is subject to<br />
these guidelines,” she said. “Therefore, urban<br />
farmers, community gardens and backyard<br />
gardeners should all read and implement<br />
these guidelines before offering food for<br />
public consumption, whether by sale or by<br />
donation.”<br />
Increases Nutrient Uptake Efficiency<br />
Increases Yield for a Bountiful Crop<br />
Decreases Saline Stress<br />
Improves Environment for Soil<br />
Microbial Activity<br />
Conventional and <strong>Organic</strong> Products Available<br />
Clearing Things Up<br />
The laws and standard operation procedures<br />
in the guide were previously difficult to find<br />
and navigate. Sowerwine said that this guide<br />
provides a “one-stop-shop” for laws that may<br />
affect the urban farm as well as best practices<br />
for safe growing, distribution and storage of<br />
not only fresh produce, but also eggs, chicken<br />
and small livestock. It also provides guidelines<br />
and resources for safe compost production,<br />
application and management.<br />
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SEASOL<br />
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<strong>April</strong>/<strong>May</strong> <strong>2021</strong> www.organicfarmermag.com 27
Vertical urban farm in Los Angeles. Some urban farms, depending on the operation, are<br />
fully or partially exempt from certain laws under the Food Safety Modernization Act.<br />
Continued from Page 27<br />
“[Urban farm produce] was not necessarily<br />
considered an “approved source”<br />
for sale to retail food establishments,”<br />
she said. “Two laws cleared that up.<br />
Now urban growers are considered<br />
“approved source” through a category<br />
called “community food producers”<br />
established by California state laws AB<br />
1990 and AB 234.”<br />
Sowerwine said that the COVID-19<br />
pandemic has contributed to an increase<br />
in household food production<br />
as evidenced by the rapid decline in<br />
seed supplies, and rising demand in<br />
raising chickens in backyards. This has<br />
given more incentive for people to not<br />
only become urban growers but to also<br />
be aware of any laws or acts that may<br />
pertain to them.<br />
“Many are sharing foods with their<br />
neighbors, donating it to food pantries,<br />
aggregating produce into CSA-type<br />
boxes, and some are taking advantage<br />
of the Community Food Producer Act<br />
to sell their products,” Sowerwine said.<br />
Importance of Food Safety<br />
The entire guide is structured around<br />
the necessity for food safety in an urban<br />
environment. Urban farmers need<br />
to adhere to any and all food safety<br />
laws that may apply to their operation,<br />
namely those relating to soil health<br />
and disease prevention in order to<br />
grow and sell products.<br />
“Food safety is very important in the<br />
urban farming sphere, particularly in<br />
relation to urban soils,” Sowerwine<br />
said. “It is important before starting<br />
to farm to assess your urban soils for<br />
any risk of contamination by learning<br />
about the prior site use, and if there is<br />
elevated risk, then getting a soil test.”<br />
The guide outlines testing, remediation<br />
and best management practices for<br />
urban soils.<br />
Another issue is disease prevention.<br />
The guide makes it clear that following<br />
standard operating procedures is<br />
necessary to ensure that every biosecurity<br />
measure is met to reduce any and<br />
all incidence, whether that be between<br />
animals or zoonotic.<br />
“Even one case of E. coli or Salmonella<br />
is too many,” Surls said. “Everyone<br />
who produces food for distribution<br />
wants it to be healthy for whomever is<br />
going to eat it. Growers can face legal<br />
liability if someone gets sick from eating<br />
what they grew, and of course we<br />
want to prevent that from happening.”<br />
Surls said that urban farmers are generally<br />
focused on community health<br />
and food access, so the incentive for<br />
following proper guidelines to keep<br />
food production constant is there.<br />
“Everyone wants to be healthy, and<br />
following the best practices outlined<br />
will help minimize the risk of on-farm<br />
or in-garden contamination.”<br />
On-Farm Assessment<br />
At the end of the guide, Sowerwine<br />
prepared an on-farm food safety<br />
assessment for California urban farms.<br />
According to Sowerwine, the checklist<br />
offers a comprehensive assessment of<br />
potential on-farm food safety risks,<br />
adapted from USDA guidelines and<br />
in compliance with the CDFA Food<br />
Safety Guidelines, yet “tailored to<br />
smaller-scale operations,” she said.<br />
“It covers the five main areas of potential<br />
risk of contamination and how to<br />
assess them, including risk from water,<br />
animals, soils, surfaces and health and<br />
hygiene factors, and best practices to<br />
minimize risk as well sample record<br />
keeping forms to document best practices,”<br />
she said.<br />
Sowerwine noted that even for smaller-scale<br />
operations, it can be helpful<br />
to walk through the assessment and<br />
determine where there may be contamination<br />
issues and how to address<br />
them.<br />
“And for farms that may have community<br />
or student engagement, what<br />
kind of signage and training may be<br />
beneficial,” she added.<br />
A publication of the full guide is available<br />
for free download at anrcatalog.<br />
ucanr.edu/pdf/8660.pdf.<br />
Comments about this article? We want<br />
to hear from you. Feel free to email us at<br />
article@jcsmarketinginc.com<br />
28 <strong>Organic</strong> <strong>Farmer</strong> <strong>April</strong>/<strong>May</strong> <strong>2021</strong>
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HOW TO HELP<br />
ENDANGERED POLLINATORS<br />
WHILE ALSO HELPING YOUR FARM<br />
By DANITA CAHILL | Contributing Writer<br />
No milkweed means no monarch caterpillar food, according to McKibbin (photo courtesy Kitty Bolte, Xerces Society.)<br />
As a result of human activity, the<br />
world has lost about half of its<br />
insect populations in the last 75<br />
years. Those insect declines are due<br />
largely to habitat loss and degradation,<br />
pesticides and climate change, said Jessa<br />
Kay-Cruz of the Xerces Society for Invertebrate<br />
Conservation. Some of those<br />
insects can be important pollinators for<br />
crop production, such as the monarch<br />
butterfly.<br />
“Monarchs across the U.S. are imperiled,<br />
though the Western population is<br />
worse off than the Eastern population,”<br />
said Sarah McKibbin, Restoration<br />
Project Manager of Solano Resource<br />
Conservation District (RCD).<br />
“Monarchs are completely dependent<br />
on milkweed plants,” said McKibbin,<br />
who was a speaker for a recent online<br />
workshop sponsored by Solano.<br />
The butterflies lay their eggs on milkweed<br />
plants. When the eggs hatch, the<br />
caterpillars eat only milkweed.<br />
“The toxins in milkweed helps protect<br />
them from predators,” she said.<br />
Adult monarch on narrow-leaf milkweed, A. fascicuaris . In 2020, the Western Monarch Thanksgiving<br />
Count tallied only 1,914 monarchs (photo courtesy Stephanie McKnight/Xerces Society.)<br />
The milkweed flowers provide a nectar<br />
source, not only for adult monarchs,<br />
but for other pollinators too, such as<br />
native bees. “Milkweed is a relatively<br />
prolific nectar supplier,” McKibbin said<br />
The monarch caterpillars go through<br />
30 <strong>Organic</strong> <strong>Farmer</strong> <strong>April</strong>/<strong>May</strong> <strong>2021</strong>
Monarch caterpillar on woolypod milkweed, A. eriocarpa .There are multiple native milkweed species available for planting<br />
(photo courtesy Brianna Borders/Xerces Society.)<br />
five instar stages (between molts) before<br />
forming a chrysalis and attaching<br />
it to a milkweed stem. The monarch<br />
lifecycle repeats four to five times each<br />
spring through fall. The last batch of<br />
butterflies that emerge are the ones<br />
that migrate from parts of the U.S. and<br />
Canada.<br />
“Western monarchs overwinter along<br />
the California coast in Monterey pines<br />
and eucalyptus trees,” McKibbin said.<br />
“Eastern monarch populations overwinter<br />
in Mexico in Oyamel fir trees.”<br />
Monarch Numbers<br />
In the 1980s, there were an estimated<br />
4.5 million monarchs that overwintered<br />
along the Pacific Coast. In 2019, the<br />
number had dropped to approximately<br />
29,000, and in 2020, the Western Monarch<br />
Thanksgiving Count tallied only<br />
1,914 monarchs.<br />
“Western monarchs have declined by<br />
over 99%,” McKibbin said. “The East-<br />
Continued on Page 32<br />
<strong>April</strong>/<strong>May</strong> <strong>2021</strong> www.organicfarmermag.com 31
Incorporating native milkweed species into cover crops can create a habitat for monarchs while reducing the need for<br />
broad-spectrum insecticides.<br />
Continued from Page 31<br />
ern monarchs have ‘only’ declined by<br />
80% in the past 20 years.”<br />
So why are the Western monarchs in<br />
such rapid decline? The reasons are<br />
many, according to Solano RCD:<br />
• Loss of overwintering habitat.<br />
• Development along the Pacific<br />
coastline.<br />
• Decline and aging of pine and eucalyptus<br />
groves without regeneration.<br />
• Breeding habitat loss and degradation.<br />
• Urban sprawl.<br />
• Agricultural practices with extensive<br />
tilling and pesticide use.<br />
• Pesticides used for mosquito control.<br />
• Pesticides used by homeowners and<br />
the nursery trade.<br />
• Widespread pesticide contamination<br />
“ Don’t plant milkweed within<br />
five miles of the coast<br />
because it can interrupt the<br />
monarch’s life cycle.<br />
− Sarah McKibbin, Solano RCD<br />
”<br />
of milkweed.<br />
• Climate change – causing changes<br />
in temperature and rainfall patterns<br />
which affects monarch migration and<br />
milkweed distribution.<br />
• Tropical milkweed, which is not<br />
native and can harbor a parasite<br />
harmful to monarchs.<br />
“Good” vs. “Bad” Milkweed<br />
So, what is the difference between milkweed<br />
that is harmful to monarchs and<br />
milkweed that is beneficial? Tropical or<br />
exotic milkweed, Asclpias curassavica,<br />
is harmful. It grows north to Mexico<br />
but isn’t native to the U.S. or Canada.<br />
It’s an attractive plant and easily grown,<br />
so it is most often the species offered<br />
for sale in nurseries. Tropical milkweed<br />
blooms and grows year-round in mild<br />
climates – except in the case of rare<br />
freeze events. Because of its year-round<br />
availability, tropical milkweed convinces<br />
the monarch to continue breeding<br />
throughout the winter.<br />
Nature didn’t intend for monarchs to<br />
breed year-round, and there are several<br />
risks involved when they do, according<br />
to Monarch Joint Venture (MJV),<br />
University of Minnesota. Risks include<br />
a higher OE infection rate and frigid<br />
temperatures during those rare freezing<br />
events. There is also a chance of food<br />
shortages when caterpillars eat tropical<br />
milkweed to the ground during the<br />
winter and there is no native milkweed<br />
available because of winter dieback.<br />
When gardeners and growers in the<br />
coastal southern U.S. and California<br />
plant non-native tropical milkweed,<br />
there is another potential risk to the<br />
monarch. Milkweed harbors a debilitating<br />
parasite, a protozoan called Ophy-<br />
32 <strong>Organic</strong> <strong>Farmer</strong> <strong>April</strong>/<strong>May</strong> <strong>2021</strong>
ocystis elektroscirrha (OE). Patches of<br />
tropical milkweed growing year-round<br />
can foster greater transmission of OE,<br />
according to MJV, although another<br />
study shows that tropical milkweed can<br />
lower OE replication. This is because of<br />
elevated levels of cardenolide toxins (a<br />
type of heart-arresting steroid) in the<br />
plant. But less OE replication still may<br />
not be in the monarch’s favor. Instead of<br />
dying quickly, butterflies that are moderately<br />
infected could potentially spread<br />
more disease over a longer life span.<br />
Adult monarchs infected with OE can<br />
harbor thousands, even millions, of<br />
microscopic spores on their bodies.<br />
Infected butterflies scatter the dormant<br />
spores onto eggs or milkweed leaves.<br />
These in turn are ingested by monarch<br />
caterpillars. The spores replicate inside<br />
the larvae and pupae. Heavily infested<br />
monarchs may not emerge completely<br />
from their chrysalis. They either<br />
become stuck or are too weak to fully<br />
open their wings. Monarchs with milder<br />
infections of OE can’t fly as well and<br />
don’t live as long as healthy butterflies.<br />
North America’s native milkweeds<br />
show dieback in the winter, which stops<br />
the winter breeding and resets the population<br />
of OE. If you have any tropical<br />
milkweed, MJV suggests cutting it back<br />
in the fall and winter months and gradually<br />
replacing it with native milkweed<br />
species. The natives include narrow-leaf<br />
milkweed, Asclpias fascicuaris; showy<br />
milkweed, A. speciosa; California<br />
milkweed, A. Californica; heartleaf<br />
milkweed, A. cordifolia; and woolypod<br />
milkweed, A. eriocarpa.<br />
Other milkweed notes: “Don’t plant<br />
milkweed within five miles of the coast<br />
because it can interrupt the monarch’s<br />
life cycle,” McKibbin said.<br />
Continued on Page 34<br />
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Continued from Page 33<br />
The toxin in milkweed concerns ranchers, but it takes a<br />
long ingestion period before it harms cattle. “There are no<br />
recent reported deaths of cattle to USDA from milkweed,”<br />
McKibbin said.<br />
Helping Adult Monarchs and Other Pollinators<br />
Besides native milkweed, there are other plantings that<br />
farmers can grow to attract monarchs as well as native bees<br />
and other pollinators. Plant a variety of nectar sources and<br />
plan your flowering selections so they produce year-round<br />
bloom.<br />
McKibbin suggests practicing the 10-10-10-10-1 rule:<br />
• Plant a 10’ X 10’ area (minimum).<br />
Monarch chrysalis on narrow-leaf milkweed, A. fascicuaris.<br />
Planting milkweed within five miles of the coast can interrupt<br />
the monarch’s life cycle, according to McKibbin (photo courtesy<br />
Stephanie McKnight/Xerces Society.)<br />
• Include at least 10 native milkweed plants of the same<br />
species.<br />
• Plant a total of at least 10 different plant species.<br />
• Plant each species in a block at least one square meter in<br />
size.<br />
• Other ways to help pollinators is to shop mindfully −<br />
buy organic produce and organic nursery stock.<br />
“Avoid products that contain GMO ingredients, especially<br />
corn, wheat, and soy. These are the most common<br />
‘Roundup-ready’ GMO crops that allow farmers to spray<br />
entire fields with roundup to kill all plants except their<br />
crop, including wild milkweed. Milkweed that would have<br />
grown wild in fields and farm edges are collateral damage,<br />
so GMO crops are a large contributor to habitat loss in<br />
agricultural settings – no milkweed means no monarch<br />
caterpillar food,” McKibbin said.<br />
Protect monarch overwintering sites. Volunteer for citizen<br />
science projects. Get involved with the Thanksgiving and<br />
New Year’s monarch counts. Donate to nonprofits that are<br />
helping to protect monarchs and other pollinators. Avoid<br />
pesticides, especially systemic insecticides such as neonicotinoids.<br />
“They are the worst,” McKibbin said. “They can affect plants,<br />
water and soils for months to years.”<br />
Tomato field hedgerow (photo courtesy of Kitty Bolte/Xerces<br />
Society.)<br />
For more information on helping monarchs and other beneficial<br />
insects visit the following websites: Solano Resource<br />
Conservation District: https://www.solano.org, Xerces<br />
Society: https//xerces.org, Monarch Joint Venture: https//<br />
monarchjointventure.org.<br />
Comments about this article? We want to hear from you.<br />
Feel free to email us at article@jcsmarketinginc.com<br />
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USDA National <strong>Organic</strong><br />
Program Changing<br />
Approach to <strong>Organic</strong><br />
Oversight in India<br />
By TAYLOR CHALSTROM | Assistant Editor<br />
USDA is increasing its oversight in<br />
the Indian organic market to better<br />
monitor organic products coming<br />
into the United States.<br />
On Jan. 11, <strong>2021</strong>, USDA notified India’s<br />
Agricultural and Processed Food Products<br />
Exports Development Authority<br />
(APEDA) that they are ending U.S.-India<br />
<strong>Organic</strong> Recognition. The decision<br />
comes as USDA deemed India’s organic<br />
control system unable to adequately protect<br />
the integrity of the USDA organic<br />
seal.<br />
The previous agreement between USDA<br />
and APEDA allowed APEDA-accredited<br />
certifiers to provide USDA organic<br />
certification in India, according to the<br />
USDA website (ams.usda.gov/services/<br />
organic-certification/international-trade/India).<br />
USDA is altering the agreement so that<br />
all India organic products/ingredients<br />
across the entire supply chain are to<br />
be certified as USDA organic with<br />
a USDA National <strong>Organic</strong> Program<br />
(NOP) certificate in order to come to the<br />
U.S. starting July 12, 2022. USDA will<br />
allow a one-and-a-half-year transition<br />
period for India organic suppliers and<br />
U.S. buyers in order to help minimize<br />
market disruption as a result of the<br />
new requirements. During this period,<br />
organic operations previously certified<br />
by APEDA-accredited certifiers will be<br />
allowed to apply for direct certification<br />
to NOP by USDA-accredited certifiers.<br />
The exact timeline of the transition period,<br />
according to USDA, is as follows:<br />
• Jan. 11, <strong>2021</strong>: APEDA notified<br />
of an end to U.S.-India <strong>Organic</strong><br />
Recognition.<br />
• March <strong>2021</strong>: Certifiers are to report<br />
any certification applicants who<br />
are currently certified by APEDA<br />
in India in the <strong>Organic</strong> Integrity<br />
Database (public data). This will<br />
help U.S. buyers verify that a farm<br />
or business in India has applied for<br />
NOP certification.<br />
• July 12, <strong>2021</strong>: Any India organic<br />
business wanting to export to the<br />
U.S. must have applied for USDA/<br />
NOP certification.<br />
• July 12, 2022: To export to the U.S.,<br />
all India organic products/ingredients<br />
across the supply chain must<br />
be certified USDA organic with a<br />
USDA/NOP certificate.<br />
<strong>Organic</strong> businesses in the U.S. buying<br />
from an India organic supplier certified<br />
by an APEDA-accredited certifier must<br />
communicate with those suppliers about<br />
the need to apply for NOP certification<br />
to a USDA-accredited certifier by July<br />
12, <strong>2021</strong>. USDA states that USDA-accredited<br />
certifiers may issue USDA/NOP<br />
certification to any organic business verified<br />
to fully comply with USDA organic<br />
regulations throughout the transition<br />
period.<br />
India organic suppliers cannot continue<br />
business with U.S. buyers after July 12,<br />
<strong>2021</strong> if they do not apply for the NOP<br />
certification. The <strong>Organic</strong> Integrity Database<br />
will need to be used by buyers to<br />
verify existing certification or a pending<br />
application with a USDA-accredited<br />
certifier. The database can be accessed at<br />
organic.ams.usda.gov/Integrity/.<br />
<strong>Organic</strong> suppliers in India that are certified<br />
by an APEDA-accredited certifier<br />
will need to identify USDA-accredited<br />
certifiers previously approved under<br />
the U.S.-India recognition agreement.<br />
To accomplish this, visit apeda.gov.in/<br />
apedawebsite/organic/NPOP_certification_bodies.pdf<br />
and refer to the “Validity<br />
of Current Accreditation” and “Scope<br />
of Accreditation” columns. Suppliers<br />
that do not apply for certification by July<br />
12, <strong>2021</strong> will be barred from exporting<br />
USDA organic products to the U.S.<br />
India suppliers currently accredited<br />
by APEDA for USDA certification may<br />
apply to the USDA National <strong>Organic</strong><br />
Program (NOP) for direct accreditation<br />
at any time.<br />
Comments about this article? We want<br />
to hear from you. Feel free to email us at<br />
article@jcsmarketinginc.com<br />
36 <strong>Organic</strong> <strong>Farmer</strong> <strong>April</strong>/<strong>May</strong> <strong>2021</strong>
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MICRONUTRIENTS:<br />
Effective Measurement<br />
and Use of Manganese<br />
Part Two: Interpreting Lab Results for Manganese<br />
By NEAL KINSEY | Kinsey Ag Services, Contributing Writer<br />
This article is the second in a two<br />
part series on the micronutrient<br />
manganese. See the February/<br />
March issue of <strong>Organic</strong> <strong>Farmer</strong> magazine<br />
for additional information on<br />
manganese.<br />
A close reading of the information<br />
provided in Part 1 of this article series<br />
and elsewhere should make it evident<br />
that testing for manganese levels can be<br />
measured and reported with great variance<br />
from lab to lab. Consequently, the<br />
required numbers can be very different<br />
on other tests than those that are being<br />
discussed here.<br />
The guidelines used below for manganese<br />
needs and recommendations<br />
are based on tests for evaluating soils<br />
analyzed by using the originally established<br />
needs for the Albrecht system.<br />
Some may object and question why one<br />
would report numbers that are not of<br />
universal application. When numbers<br />
vary so greatly, nothing is meaningful<br />
unless it can be based on a foundation<br />
that is solid enough to report what field<br />
testing shows to be actually needed.<br />
Manganese Deficiencies<br />
What should growers look for to help<br />
identify when manganese is deficient<br />
(less than 40 ppm on the true Albrecht<br />
system tests) and limiting for the crop<br />
being grown on such soils? Numbers<br />
reported by other soil laboratories are<br />
not comparable according to those who<br />
have tried to do so. This is just to caution<br />
that pushing up the numbers on<br />
other soil tests to match what is shown<br />
as the measured need for crop examples<br />
used here may result in the overuse<br />
of manganese.<br />
But when this specific test is performed,<br />
40 ppm is the minimum recommended.<br />
Soybeans will begin to show mild<br />
symptoms of manganese deficiency<br />
in mature leaves later in the season at<br />
37 to 38 ppm. Levels of 30 ppm or so<br />
begin to show results of shorter stalks<br />
of corn, though less yield and stalk size<br />
should be expected to result long before<br />
that. This makes manganese deficiency<br />
especially important for attaining the<br />
highest tonnages of corn silage.<br />
38 <strong>Organic</strong> <strong>Farmer</strong> <strong>April</strong>/<strong>May</strong> <strong>2021</strong>
Once other obvious deficiencies have<br />
been eliminated, wheat yields tend to<br />
respond well as manganese builds to<br />
the higher levels in any soil. For example,<br />
soils with similar fertility that have<br />
40 ppm manganese will not produce<br />
the yield that those same soils provide<br />
at 80 ppm manganese. In fact, when<br />
manganese is truly the most limiting<br />
factor for high-yielding wheat soils, the<br />
yields will continue to increase on those<br />
soils until 200 to 250 ppm available<br />
manganese is reached when this specific<br />
type of testing is performed. Caution<br />
is extremely necessary here as almost<br />
any textbook will report that 200 ppm<br />
manganese is toxic to growing plants.<br />
Obviously, the tests being used are not<br />
the same as the one advocated here for<br />
determining manganese availability.<br />
Tree crops, especially nut trees, respond<br />
very well to manganese with<br />
best results on soils where manganese<br />
is above 120 ppm. Walnuts are especially<br />
sensitive to manganese deficiency.<br />
Consequently, though normally not<br />
specifically recognized as the problem,<br />
soils that test below 40 ppm using this<br />
particular type of testing for manganese<br />
are generally classified as being<br />
unfit for walnut production.<br />
The guidelines given here for manganese<br />
are specific to this type of testing,<br />
and using them is not advised for any<br />
other laboratory’s manganese test. But<br />
these numbers are being provided here<br />
to show there is a basic foundation to<br />
explain what can be expected when<br />
manganese is properly measured and<br />
applied for crop production.<br />
Anything less than 40 ppm on the test<br />
we use means the full benefits from<br />
adequate manganese will not be realized<br />
for whatever crop. Although on<br />
soils with more than 5% organic matter,<br />
resulting deficiencies may not be as<br />
evident, and optimum results will still<br />
not be attained until any manganese<br />
deficiency is corrected.<br />
In addition, keep in mind that a true<br />
manganese deficiency of below 40 ppm<br />
may be the case, and manganese still<br />
may not give the expected response<br />
when applied and even brought up to<br />
above the deficiency level. That is why<br />
so many “research” plots concerning<br />
manganese use fail to provide any benefits.<br />
If any of the primary or secondary<br />
elements are seriously deficient, correcting<br />
them will take precedence over<br />
the manganese level.<br />
For example, a serious problem with<br />
newly planted almond trees is breakage<br />
during high winds. Some growers<br />
have corrected that problem by adding<br />
sufficient amounts of manganese. Many<br />
others try it without the same satisfactory<br />
results. That is because there<br />
are three elements involved here that<br />
Continued on Page 40<br />
<strong>April</strong>/<strong>May</strong> <strong>2021</strong> www.organicfarmermag.com 39
Continued from Page 39<br />
provide for increased wood strength of<br />
which manganese is usually found to be<br />
correctly ranked as the second or third<br />
most important.<br />
Adequate potassium is always of primary<br />
importance for wood strength.<br />
Manganese is second if it is below 40<br />
ppm. Sufficient copper, which will be<br />
considered next in this series, is the<br />
other needed element and is necessary<br />
to help provide strength and resilience<br />
to the limbs.<br />
Without an adequate uptake of manganese,<br />
weaker wood will always be the<br />
result. But soils can have good to excellent<br />
manganese levels and still the trees<br />
or other crops that grow there can be<br />
deficient in manganese. This becomes<br />
a serious problem when soils are too<br />
high in potassium (generally on lighter<br />
soils where too much compost has<br />
been applied) or too high in sodium (a<br />
problem for many soils, especially in<br />
the Western U.S.)<br />
In fact, in any combination where<br />
potassium and sodium added together<br />
exceeds 10% of total soil saturation,<br />
manganese uptake begins to be blocked.<br />
The higher that percentage goes above<br />
10%, the worse this problem becomes<br />
for the growth of any crop.<br />
Note that the soil test may show to have<br />
plenty of manganese, but remember<br />
that, in this case, manganese is still<br />
there and in the correctly available<br />
form. That is because potassium and<br />
sodium do not tie up the manganese.<br />
Between the two when their levels of<br />
soil saturation is too high (10% on<br />
the Albrecht test), then, the uptake of<br />
sufficient manganese is blocked out.<br />
There is so much available potassium or<br />
sodium there that sufficient manganese<br />
just cannot get into the plants.<br />
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Having Sufficient Manganese<br />
Why be concerned about having sufficient<br />
manganese in the soil? What are<br />
the benefits to farmers and growers<br />
when manganese-deficient soil is adequately<br />
corrected?<br />
First, sufficient manganese (above 40<br />
ppm) is necessary for quicker seed<br />
germination. Accordingly, enough<br />
manganese will cause the plants to<br />
grow off faster. Manganese is needed<br />
to determine the number of seed to<br />
be produced and to hold the blooms<br />
and seed or fruit in place. So, adequate<br />
manganese is needed from start to<br />
finish in terms of crop production.<br />
What levels are needed? 40 ppm is the<br />
minimum. 80 ppm is considered as<br />
good. 125 ppm is considered the low<br />
side of excellent and 200 to 250 the<br />
high side, depending on crop sensitivity.<br />
In any case, it is best to build the level<br />
up in increments, even if the cost to do<br />
so is not considered as being a problem.<br />
The guidelines for application rates<br />
on manganese is a maximum of 200<br />
pounds of 28% manganese sulfate per<br />
acre even when severe deficiencies will<br />
not be corrected by that amount.<br />
There is yet another problem that growers<br />
may have in trying to determine<br />
when there is sufficient manganese for<br />
the crop. This has to do with using a<br />
leaf analysis to determine if plants have<br />
sufficient or insufficient manganese.<br />
One good example is when the Albrecht<br />
analysis shows manganese as<br />
even slightly deficient, common scab<br />
can be a problem for potatoes. Yet, in<br />
too many cases, the leaf analysis shows<br />
the level of manganese to be adequate,<br />
even when the soil test still shows manganese<br />
as deficient in the soil. Which<br />
should be believed? The fact that this<br />
problem is never solved until adequate<br />
manganese is present in those soils<br />
should help show which is correct!<br />
Keep in mind that many potato growers<br />
use a metallic manganese based<br />
foliar to treat for disease. This can<br />
40 <strong>Organic</strong> <strong>Farmer</strong> <strong>April</strong>/<strong>May</strong> <strong>2021</strong>
‘<br />
Manganese is needed<br />
to determine the<br />
number of seed to be<br />
produced and to hold<br />
the blooms and seed<br />
or fruit in place. So,<br />
adequate manganese<br />
is needed from start to<br />
finish in terms of crop<br />
production.<br />
’<br />
greatly skew the levels shown from the<br />
leaf test. But this is not the entire story.<br />
Potatoes have been used as an example<br />
here due to their extreme sensitivity to<br />
manganese deficiency. And at times,<br />
even those who have not used a foliar<br />
manganese can have leaf tests that<br />
show manganese as “too high” when, in<br />
actuality, the soils are still too deficient<br />
to correctly supply plant needs.<br />
We find this consistently tends to be the<br />
case with leaf testing for most micronutrients,<br />
not just manganese, as compared<br />
to the levels shown to be required<br />
on the soil test to properly solve each<br />
deficiency. Such deviations can also be<br />
a serious problem when considering<br />
needs for other manganese-sensitive<br />
crops such as wheat, grapes and all<br />
types of trees, but especially English<br />
walnuts and black walnuts.<br />
There is still another precaution that<br />
should be considered when using a leaf<br />
analysis for evaluating available levels<br />
of manganese for crop production.<br />
Even leaving dust on the leaves can<br />
cause manganese levels to appear to be<br />
too high in the plant. A good way to<br />
detect this is when iron and aluminum<br />
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Continued from Page 41<br />
are also shown to be extremely high on<br />
the same analysis. When that happens,<br />
test again with clean plant tissue to be<br />
sure.<br />
Another factor that is essential for<br />
manganese uptake is that a sufficient<br />
supply of calcium must be present in<br />
the soil. This is not determined by the<br />
fact that the soil has an adequate to<br />
high pH. There is only one way to tell<br />
when soils have at least the minimum<br />
level of available calcium to take up<br />
sufficient manganese for the crop: the<br />
soil needs calcium levels to be built up<br />
to and then maintained at between 60%<br />
to 70% base saturation before plants<br />
can most efficiently utilize available<br />
manganese from the soil. (CAUTION:<br />
Some labs may test as much as 4% lower<br />
while others show as much as 12%<br />
higher soil calcium saturation than the<br />
numbers determined by the Albrecht<br />
system testing procedures.)<br />
Perhaps an additional word of caution<br />
should be given here, for even soils that<br />
may initially have an adequate amount<br />
of manganese can develop a deficiency<br />
problem if an excessive amount of unneeded<br />
lime is applied. An excess can<br />
cause manganese to go from adequate<br />
to deficient over the next one to three<br />
cropping seasons.<br />
This can happen when any material<br />
containing a sufficient amount of calcium<br />
is applied on soils that barely have<br />
enough manganese (with even worse<br />
results when the soil is already deficient<br />
in manganese), because when calcium<br />
is applied, as it becomes available over<br />
the next one to three years, it will begin<br />
to tie up plant-available manganese in<br />
that soil. If the soil has enough manganese<br />
to stand the amount of calcium<br />
applied, manganese will not become<br />
a problem there as a result of applying<br />
needed lime.<br />
This is one reason why in some areas<br />
potato growers can apply calcium<br />
limestone and have no problem with<br />
common scab, but in other areas no<br />
one will dare apply it. And due to soils<br />
needing calcium for adequate uptake<br />
of all the other nutrients (including<br />
N-P-K) if the problem is not solved,<br />
crop production will not only suffer<br />
but may even decline in terms of yield<br />
and certainly in terms of food quality.<br />
Yet the issue of adequate manganese in<br />
the soil can be overcome by applying<br />
a sufficient amount of the correct type<br />
of manganese. That needed amount<br />
should be based on a detailed soil<br />
analysis which can accurately determine<br />
the desired level in the soil. The<br />
test should be such that it can accurately<br />
determine how much manganese<br />
is required to overcome any tie-up<br />
from added calcium as well. Whether<br />
already deficient, or for a potential<br />
decrease in manganese due to liming<br />
or other sources of calcium (such as<br />
poultry manure), only the use of true<br />
manganese sulfate should be considered<br />
for adding to the soil to sufficiently<br />
build up the manganese level to solve<br />
that need.<br />
MyAgLife Da<br />
From the tests we use, the need for<br />
manganese will be reflected and solved<br />
based on the use of one pound of actual<br />
manganese for every pound shown to<br />
be lacking. If that does not happen in<br />
the next twelve months after an initial<br />
application, someone is likely providing<br />
the wrong advice or recommending the<br />
wrong product.<br />
Some soils do not even build well using<br />
manganese sulfate. In a very few cases<br />
it has been necessary to apply the needed<br />
amount for two or three years in a<br />
row to reach the desired minimum level.<br />
Because of its physiological make-up,<br />
a crop which can also help to measurably<br />
increase manganese availability in<br />
the soil is rice.<br />
Just keep in mind that the primary<br />
elements, N-P-K, truly are primary in<br />
terms of getting enough nutrients there<br />
to grow the crop. But when any one of<br />
these three are over-applied, providing<br />
more than the soil can tolerate, those<br />
Compacted low-calcium soils reduce manganese<br />
availability for walnuts (photo by N. Kinsey.)<br />
same elements can cause a whole new<br />
set of problems, not just for the crops<br />
mentioned in this article but for all<br />
types of crops and growing plants.<br />
For example, as discussed already in<br />
regard to manganese, potassium or<br />
sodium alone, or any combination of<br />
the two, totaling more than 10% will<br />
begin to block the uptake of manganese.<br />
Normally, available soil boron<br />
will begin to be tied up when potassium<br />
remains above 7.5% saturation in any<br />
soil during the growing season. Excessive<br />
phosphate reduces zinc availability<br />
and uptake in crops. And excessive<br />
nitrogen ties up available copper, which<br />
is the next micronutrient that will be<br />
considered in this series about the need<br />
for trace elements.<br />
Comments about this article? We want<br />
to hear from you. Feel free to email us at<br />
article@jcsmarketinginc.com<br />
42 <strong>Organic</strong> <strong>Farmer</strong> <strong>April</strong>/<strong>May</strong> <strong>2021</strong>
ily News Report<br />
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44 <strong>Organic</strong> <strong>Farmer</strong> <strong>April</strong>/<strong>May</strong> <strong>2021</strong>