By now, you should have received the blank Farmland Assessment application packet from your local tax assessor. Regardless if that has happened, we urge all clients to contact us to get your annual application paperwork completed and certified. Our instructions to our clients (including a schedule of fees, and cutoff for our discount) can be read by clicking here. Our calendar showing our availability and office hours can be found by clicking here. A worksheet to help you organize your information is found by clicking here. Lastly, directions can be found here.
Please know that there is no extension possible for that August 1 deadline. We look forward to seeing you soon.
Health and Safety Alert: Emerald Ash Borer
Written by Steve Kallesser
Since 2002, we have watched the progressive spread of the invasive insect, the Emerald Ash Borer (EAB), from the first discovery of the beetle in Michigan, to the recent discovery of the insect in New Jersey, in the spring of 2014. Today, EAB is present throughout the Gracie & Harrigan service area.
Recently, the New Jersey EAB situation took a dangerous turn as the first known injury by an EAB-infested tree occured at Monmouth Battlefield State Park. Ash trees are known to become abnormally brittle shortly after their death. EAB infestations begin in the top of the tree, and ash trees have normally been infested for 3 years before symptoms become noticeable to people on the ground. So, when a chainsaw sends vibrations up the tree as it is being cut down, it is not uncommon for limbs and branches to break off and fall down upon or near the cutter.
The risk to landowners and arborists is real. We have been told that at least two New Jersey tree services are refusing to cut down dead ash trees, out of concern for their workers' safety.
We urge clients with white ash trees within striking distance of their homes, utility lines, outbuildings, playgrounds, etc. to address the ash trees before they begin showing symptoms. (Ash trees out in the woodlot that are not within striking distance of commonly used hiking trails could be left for woodpecker and other wildlife habitat.)
It is estimated that 95 to >99% mortality will occur among our native white ash population. There is no known treatment within the forest, however, individual specimen trees in yards and along roadways can be treated with an insecticide that is watered into the roots of the tree on a yearly or biannual basis by a homeowner or a tree service, or through bark or root injection by a qualified professional. Now is the time to begin treatment of specimen trees.
What can be done in your woodlot now? For areas of the forest with a high concentration of ash trees, consideration should be given toward how you want your forest to be post-EAB. Plans should begin for invasive species control, to prevent unwanted proliferation of invasives following EAB mortality. Planting and protecting native tree seedlings will help to establish new tree growth, which will help to transition the forest following ash mortality.
Why Do We Do That? Forest stand improvement explained
Written by Steve Kallesser
Forest stand improvement is a very common recommendation under forest management plans that we write, but what is their ecological basis? Forest stand improvement thinnings can take many forms. Most commonly they are either thinning from below or crop tree management.
By thinning from below foresters are seeking to mimic low- to moderate-intensity wildfires. Such wildfires were common hundreds of years ago and helped shape the forest that we know today. By favoring thick-barked species such as oaks and pine, such fires helped develop native wildlife and plant communities and were an important ecological process. Of course your insurance company would likely not be happy if you started flicking matches into the forest. But by cutting thin-barked species, especially those with smaller diameters, we can get the same outcome using a slightly different process.
Crop tree management is slightly different in that we specifically identify high-quality and or high wildlife value trees that we wish to retain on the property. Next we identify lower-value trees (either economic value or ecological value) that are competing with the trees designated to remain. Some of those trees that are directly competing with residual trees are designated to be cut.
Both systems are designed to increase the health and vitality of the residual forest as well as the individual trees designated to remain. Since many of the residual trees are oaks and other thick-barked species, these methods correspond well to the outcomes of light- and medium-intensity wildfires. When such thinning is combined with competing understory vegetation control, we also have the added benefit of improving groundcover quality and improving the chances for developing new seedlings and saplings that should become the next generation of trees as the older trees die off.
As once-far-away disease problems become resident in northern and central New Jersey -- such as emerald ash borer and bacterial leaf scorch -- we are further reminded that our forests are dynamic, disturbance-dependent ecosystems. They will change whether we like it or not. By following the ecological processes that developed these forests in the first place we have our best chance for keeping them healthy in the long term.