SoMar Silvopasture Demonstration Project

Marin County

The SoMar Silvopasture field demonstration project is located in northern Marin County within the Chileno Creek and greater Walker Creek Watersheds.

Overlooking silvopasture plantings on hillside above the pond.

Regional Context/Background

Much of northwest Marin County is mixed annual-perennial grassland. Tree cover is minimal, and generally associated with certain soil types, north-facing slopes, riparian areas, or historic windbreaks. Integrated forest and grazing lands are rare, generally limited to small stands of oak or bay woodlands. 

As excessive heat days have increased in recent years, rancher concerns about heat stress to livestock have also grown. Shade trees are rare and often found along fencelines or creek corridors. Where shade does exist within pastures, livestock often crowd beneath lone trees, concentrating grazing impacts in relatively small areas. Few producers in this area have explored the possibility of adding trees to grasslands to increase shade cover and improve livestock distribution. By adding trees to grazing areas, livestock are given multiple places to retreat from heat, reducing the wear and tear on any one area.  This can ultimately encourage better livestock distribution and more even forage consumption.

By prioritizing oaks and other native tree species in silvopasture systems, managers are also provided a unique opportunity to build valuable habitat on Marin County working lands. Open woodland or savanna ecosystems—and the countless species that depend on them—are increasingly rare throughout Northern California. Silvopastures featuring native tree species mimic these ecosystems, increasing tree cover and edge habit.

There is a need to build regional knowledge about silvopasture systems, particularly “silvopasture by addition,” or adding trees to grazing systems. This demonstration will help landowners to assess trade-offs and evaluate common concerns associated with mixed agroforestry-grazing systems. For example, land managers frequently express concerns about a loss of forage with increased shade in pastures. Research tends to suggest that sparse tree canopies (less than 25% canopy cover) typically have little effect on forage production, particularly when systems feature deciduous hardwood species that cast minimal shade during the early growing season when cool-season grass growth is highest. Further, these tree canopies may harbor “islands of fertility” in semi-arid grassland: areas with higher organic matter and moisture retention where green forage lingers even after the surrounding landscape has dried out. In addition to forage impacts, concerns around efficacy and maintenance are common. This project seeks to fill this regional knowledge gap, broadening a local understanding of effective design, installation, and maintenance.

Practices Trialed

Silvopasture: The demonstration project centers around the creation of a silvopasture system by integrating trees and other woody vegetation into active grazing land. Because trees are not established at a prescribed or uniform density however, the project design may better fit the NRCS CPS 612 – Tree and Shrub Establishment: “Establishing woody plants by planting, direct seeding, or through natural regeneration.”

Trial Goals

  • Demonstrate models for the sequestering carbon in grazing lands while meeting other management and biodiversity goals
  • Increase shade for livestock in open grasslands to improve grazing distribution and reduce negative impacts associated with animal concentration
  • Enhance wildlife habitat through the integration of native woody plants into grasslands and creation of edge habitat
  • Build regional knowledge on the effective design (including species selection, spacing, slope, aspect), installation (fencing, seed baskets), and maintenance of silvopasture systems
  • Assess impacts of integrated tree cover on soil organic matter, biodiversity, forage quantity, and quality, and livestock behavior in grazing lands

SoMar Farms

SoMar Farms consists of over 600 acres of rangeland characterized by annual and perennial grasses and forbs, with scattered bay laurel trees (Umbellularia californica), coastal live oak (Quercus agrifolia), California buckeye (Aesculus californica), and eucalyptus (Eucalyptus globulus). The property primarily supports livestock grazing and finishing grass-fed beef, although the landowner also raises grass-fed lamb. The landowner is actively engaged in a variety of restoration activities on the property as a whole. They are proud to produce delicious and nutritious food for their community by using regenerative agricultural practices that prioritize the well-being of the planet, animals, and people involved.

SoMar Farms received a Carbon Farm Plan in 2018, and they have been working to accomplish goals of increased carbon sequestration including increasing year-round above-ground biomass, increasing forage quality, improving soil health and water holding capacity, and operating as a model of good stewardship and business sustainability. This practice is one of many that they are working on that work to contribute to those goals. This landowner is interested in trying new things and contributing to the “good stewardship model”, and thus was a great candidate for this demonstration project. They are excited to increase shelter for cattle from high winds and heat and look forward to the potential of observing any effects on forage within that pasture, whether directly or indirectly supported by this project.

Climate

The SoMar Silvopasture demonstration project is located in a region known locally as the “Petaluma Gap.” Characterized by rolling open grasslands, this part of northern Marin and southwest Sonoma County is characterized by gentle topography and coastal influence, including onshore wind and summer fog. A mild climate and summer fog favor annual grasslands and coastal prairies, and predominant land uses in this area are cattle grazing (typically cow-calf operations), silage production, and dairying.

  • Average annual precipitation: 41 inches
  • Temperature: Average temperatures range from 42-80°F and may reach as low as 25-30°F
  • Growing Season: The wet season typically extends an average of 8 months from October to May. The ranch is within hardiness zone 9b. While much of the ranch is typically frost-free from April-October, moisture availability limits the primary growing season on non-irrigated lands to March-July.
  • Prevailing winds: From the West and Northwest

Soils

Map Unit

Slope

Soil Texture

Organic Matter (%)

AWHC (cm/cm)

Depth to Root Restrictive Layer (inches)

140

5-15%

Loam

2.48

0.16

97

209

15-30%

Clay Loam

1.20

0.20

130

Trial Design

Establishment activities, including irrigation, weeding and browse protection, will be carried out for 3 years post installation. Pending funding, RCD staff hope to revisit this site to conduct sampling per Point Blue’s Range-C protocol. 

 

Silvopasture at SoMar Farms was designed to increase biodiversity and structural diversity by installing clusters of native trees in a rangeland system. Native tree species were selected based on adaptation to local soils and climate, and their ability to provide long-term carbon sequestration, wildlife habitat, and other ecosystem services. Ten 16’ x 16’ “pod” livestock exclosures were constructed with hog panels and t-posts. Each tree “pod” contains 5 individuals. Plants were planted via seed and nursery stock. All plants were installed with de-galvanized seed baskets to reduce predation during establishment. Species include coast live oak (Quercus agrifolia), California sycamore (Platanus racemosa), box elder, (Acer negundo), California buckeye (Aesculus californica), bay laurel (Umbellaria californica), valley oak (Quercus lobata).

Project Partners/Collaborators

  • UC Office of the President (UCOP)
  • Point Blue Conservation Science’s STRAW (Students & Teachers Restoration A Watershed) Program
  • Marin Resource Conservation District (MRCD)

Variables Measured & Recorded

Marin RCD collected baseline soil samples in Fall 2024 following Point Blue’s Range-C protocol. 15 samples were collected across both the treatment site as well as a control site with appropriate “buffer zone” from the main planting site with similar vegetation, aspect, slope, and catenal position. Sample locations were selected randomly using ArcGIS Pro to represent areas beneath future tree canopy and outside of it.  

Variable(s)

Sampling Method

Sampling Equipment Used

Timing/Frequency

Analysis Method

Sampler

Soil Bulk Density

soil core to 6 inches

AMS 2 ½“ soil core on slide hammer

Fall 2024

Oregon State University

Marin RCD

pH, EC, organic matter estimate, total C and N, nitrate-N, P, K, Mg, Ca, texture, potentially mineralizable nitrogen, active carbon, wet aggregate stability, microbial respiration

Soil sample to 12 inches

AMS 2 ½“ soil core on slide hammer

Fall 2024

Oregon State University Complete Soil Health + Microbial Biomass

Marin RCD

Plant survival, height, vigor

Visual, photographic

 

Monitored for the entirety of the summer seasons for 3 years (~1x/week)

 

Point Blue STRAW staff

Pre-Restoration, Post-Installation, and Year 1 monitoring photos. Pre-restoration photos were taken in October of 2024, while Year 1 photos were taken in September of 2025. 

Pre restoration - facing northeast
Year 1 - Facing northeast
Pre-Restoration - Facing north
Year 1 - Facing north
During Planting - Facing West
Year 1 - Facing West
Preston Duncan, Marin RCD, taking soil samples using a slide hammer in the silvopasture planting site (yellow flags are planned planting locations) in November 2024.

Challenges

Establishing native plants in a rangeland setting presents challenges from livestock pressure, especially when plants are young and most vulnerable to damage. Hog panel enclosures were built for each planting pod to provide robust protection from cattle while also facilitating easy access for establishment and monitoring activities. 

The silvopasture planting area is located on steep slopes that are not easily accessible by vehicle, particularly during planting months. This necessitated hauling all tools and materials into the individual pods on foot, requiring more labor hours to complete the project. The same access constraints applied to the maintenance and irrigation design of the project, which required installation of a 1000 ft temporary mainline to convey water to each individual pod, as typical methods of watering similar sized smaller plantings were not feasible (e.g. hand watering via a water trailer).

This area of Marin County adjacent to the coast is prone to high sustained winds, which affects plant ranges and growth forms, especially for wood species with large canopies. To mitigate this, planting locations were strategically selected to maximize leeward effects and to mirror site characteristics of local naturally-occurring tree stands, which are primarily found on north facing slopes.

Key Findings

Due to the nature of silvopasture and the effects on measured variables, this project will be sampled on a longer-term return interval (3-5 years) pending appropriate funding sources.

Pre-Restoration Data Collection (Fall 2024)

Across Control and Treatment sites Pre-Planting:

    • Soil texture was mostly loam with some sandy clay loam and clay loams.
    • Soil pH averaged 5.79
    • Organic Matter averaged 4.91%
    • Water stable aggregates averaged 53.89%
    • Ca:Mg ratio averaged 1.63
    • Bulk Density was around 1.35, which is ideal for plant growth in loamy soils (does not restrict root growth).

Contact Information

Preston Duncan, Marin RCD

preston@marinrcd.org

415.787.7440

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