صنوبر بحري

لمحة عامة

الصنوبر البحري هو الصنوبر الصلب، السريع النمو الذي يحتوي على بذور صغيرة مع أجنحة كبيرة. P. بيناستر يوجد في حوض البحر الأبيض المتوسط. وهو يفضل مناخ البحر الأبيض المتوسط، وهو مناخ بارد وشتائه ممطر وصيفه حار وجاف.

التاريخ

المنطقة الأصلية لهذا النوع من الصنوبر، صنوبر بيناستر، ينبع من حوض البحر الأبيض المتوسط، بما في ذلك شمال تونس والجزائر والمغرب.
صنوير بيناستر هو موضوع شائع في علم البيئة بسبب مشاكل نموه وانتشاره في جنوب أفريقيا على مدى السنوات ال 150 الماضية بعد أن تم استيرادها إلى المنطقة في نهاية القرن ال 17 (1685-1693). ووجد أيضا منتشراً في شبه جزيرة كيب بحلول عام 1772. في أواخر القرن الثامن عشر (1780)، تم زراعته على نطاق واسع، و في بداية القرن التاسع عشر (1825-1830)، زرع تجاريا كمورد للأخشاب ولصناعة الغابات. وتغزو فصيلة أشجار الصنوبر مساحات واسعة، وعلى وجه الخصوص نباتات فينبوس (fynbos vegetation). نباتات فينبوس هو نباتات على هيئة شجيرات معرضة للحرائق و توجد في جنوب وجنوب غرب خليج أفريقيا في دولة جنوب أفريقيا. كما توجد بوفرة أكبر بالقرب من المجاري المائية. إن التشتت، وفقدان الموائل، والخصوبة كلها عوامل تؤثر على معدل الانتشار. فتلك الفصيلة تفضل التربة الحمضية مع كثافة متوسطة إلى عالية للنباتات، ولكن يمكنها أن تنمو أيضا في التربة الأساسية بل حتى في التربة الرملية والفقيرة، حيث لا يمكن أن ينمو إلا عدد قليل من الأنواع التجارية.

الإنتشار

يمتد نطاق الإنتشار من البرتغال وشمال إسبانيا (خاصة في غاليسيا) إلى جنوب وغرب فرنسا، و شرقاً إلى غرب إيطاليا وكرواتيا وجنوباً إلى شمال المغرب. وعادة ما يحدث إنتشار النبات على إرتفاعات من منخفضة إلى معتدلة، ومعظمها من مستوى سطح البحر إلى إرتفاع 600 متر، ولكن قد يصل إلى 2000 متر في نطاقه الجنوبي بالمغرب. وترجع درجة التجزؤ العالية في التوزيع الطبيعي الحالي إلى عاملين هما: تقطع وارتفاع السلاسل الجبلية مما يؤدي إلى عزلها حتى عن أقرب السكان، والأنشاطه البشريه.

الوصف

اللحاء هو برتقالي-أحمر، سميك وشديد العمق في قاعدة الجذع، أرق إلى حد ما في التاج العلوي.
الأوراق ('الإبر') على شكل أزواج، متماسكه جدا (بعرض 2 مم )، وقد تصل إلى 25 سم طولاً، وتاخذ شكل الاوراق ما بين أخضر-مزرق إلى أخضر-مصفر . كما يتميز الصنوبر البحري بأطول وأقوى الأوراق عن جميع أنواع الصنوبر الأوروبي.
المخاريط هي على شكل مخروطي، 10-20 سم طولاً و 4-6 سم سعاتاً في قاعدة عند إغلاق، أخضر في البداية، وعند النضج تتحول إلى أحمر- بنى لامع  عند عمر 24 شهرا . كما أنها تتفتح ببطء على مدى السنوات القليلة المقبلة، أو بعد تسخينها من قبل حرائق الغابات، لإطلاق البذور، وتتفتح إلى سعة 8-12 سم.
طول البذور 8-10 ملم ، وعرضها  20-25 ملم، وهي تنتشر- بالرياح.
يرتبط الصنوبر البحري ارتباطا وثيقا بالصنوبر التركي، وصنوبر جزيرة الكناري، وصنوبر حلب، والتي تشترك جميعها في العديد من الميزات. وهو نوع غير متغير نسبيا، مع التشكل المستمر على نطاق كامل.

الاستخدامات

بالإضافة إلى استخداماته الصناعية، فالصنوبر البحري هو أيضا شجرة زينة شعبية، وغالبا ما تزرع في المتنزهات والحدائق بالمناطق ذات المناخات المعتدلة الدافئة. وقد توطنت بمناطق في جنوب إنجلترا، الأرجنتين، جنوب أفريقيا وأستراليا.

نتيجة غزو بيناستر

P. pinaster is a successful نوع مجتاح in South Africa. One of the results of its invasion in South Africa is a decrease in the تنوع حيوي of the native environment.  The increase of انقراض rates of the native species is correlated with the introduction of these species to South Africa. Invasive species occupy موطن of native species often forcing them to extinction or endangerment. For example, invasive species have the potential to decrease the diversity of native plants by 50-86% in the Cape Peninsula of South Africa. As discussed above, P. pinaster is a tree species found in shrubland in South Africa. When compared to other بيئة (فيزياء حيوية), shrublands have the largest decline of species richness when invaded by an invasive species (Z=-1.33, p<0.001). Compared to graminoids; trees, annual عشب, and creepers have a larger effect on decline of ثراء الأنواع (Z=-3.78; p<0.001).  Lastly, compared to other countries, South Africa had the largest species richness decline when faced with invasive species.  South Africa is not home to many insects and diseases that limit the population of P. pinaster back in its native موطن.  Not only is there evidence that alien plant invasions decrease biodiversity, but there is also evidence that the location of P. pinaster increases its negative effect on the species richness.
In addition, depending on the regions P.pinaster invades, P. pinaster has the potential to dramatically alter the quantity of water in the environment. If P. pinaster invades an area covered with grasses and shrubs, the water level of the streams in this area would lower significantly because P. pinaster are دائم الخضرة that take up considerably more water than grasses and shrubs all year around. They deplete جريان المياه السطحية in مستجمع مائي and water flow in rivers. This depletes the resources available for other species in the environment. P. pinaster tends to grow rapidly in riparian zones, which are areas with abundant water where trees and plants grow twice as fast and invade. P. pinaster takes advantage of the water available and consequently reduces the amount of water in the area available for other species.   The fynbos catchments on the كيب الغربية of South Africa are a habitat negatively affected by P. pinaster. Twenty-three years after planting the pines, there was a 55% decrease in streamflow in this area.  Similarly, in كوازولو ناتال there was an 82% reduction in streamflow 20 years after introducing P. pinaster to the area. In the مبومالانجا, 6 streams completely dried up 12 years after أرض عشبية were replaced with pines.  To reinforce that, there is a negative effect from the invasive species P. pinaster, these areas of dense P. pinaster were thinned and the number of trees in the area decreased. As a result, the streamflow in the fynbos catchments of the Western Cape increased by 44%. The streamflow in the Mpumalanga Province increased by 120%.  As a result of P. pinaster growth, there is often less understory vegetation for livestock grazing. Once again there was a positive effect when some of the pines were removed and agreeable range grasses were planted. The grazing conditions for the sheep of the area were greatly improved when the P. pinaster plantation was thinned to 300 trees ha-1. The invasion of P. pinaster leads to the decrease of أشجار الطبقة السفلى vegetation and therefore a decrease in ماشية.

التفاعل البيئي الذي أدي إلى التأثير الحالي على البيئة

P. pinaster is particularly successful in regions with fynbos vegetation because it is تكيف to high-intensity fires, thus allowing it to outcompete other species that are not as well adapted to high-intensity fires. In areas of fire-prone shrubland, the cones of P. pinaster will release seeds when in a relatively high-temperature environment for إنبات as a recovery mechanism. This adaptation increases the competitive ability of P. pinaster amongst other species in the fire-prone shrubland.  In a 3-year observational study done in إسبانيا, P. pinaster showed a naturally high تجدد rate. Observations showed a mean of 25.25 seedlings/m^2 within the first year and then slowly decreased the next two years due to intraspecific competition.  So not only does P. pinaster compete with other species, they also compete within their own species as well. When the height of P. pinaster increased there was a negative correlation with the number of P. pinaster seedlings, results showed a decrease in P. pinaster seedlings (r=-0.41, p<0.05).
Several other characteristics contribute to their success in the regions they have invaded, including their ability to grow rapidly and to produce small seeds with large مخروط صنوبري. Their ability to grow quickly with short juvenile periods allows them to تنافس (أحياء) many native species while their small seeds aids in their dispersal. The small seeds with large wings are beneficial for wind dispersal, which is the key to reaching new areas in regions with fynbos vegetation.   فقاريات نثر البذور  are not commonly found in mountain fynbos vegetation; therefore those species that require the aid of vertebrate dispersal would be at a disadvantage in such an environment. For this reason, the small seed, low seed wing loading, and high winds found in mountainous regions all combine to provide a favorable situation for the dispersal of P. pinaster seeds.  Without this efficient dispersal strategy, P. pinaster would not have been able to reach and invade areas, such as South Africa, that are suitable for its growth. Its dispersal ability is one of the key factors that have allowed P. pinaster to become such a successful invasive species.
In addition to being an efficient disperser, P. pinaster is known to produce راتنج, such as oily تربين or حمض دهني, which can inhibit other species within the community from growing. These راتنج are produced as a defense mechanism against حشرة predators, such as the large pine weevil. According to an experiment done in إسبانيا, the resin canal density was twice as high in the P. pinaster seedlings attacked by the weevils compared to the unattacked seedlings. Since P. pinaster has the ability to regulate their production of defense mechanisms, it can protect itself from predatory in an energy-efficient manner. The resins make the P. pinaster less vulnerable to damage from insects, but they are only produced in high concentrations when P. pinaster is under attack. In other words, P. pinaster does not waste energy producing resins in safe conditions, so the conserved energy can be used for growth or reproduction. These characteristics enhance the ability of P. pinaster survive and flourish in the areas it invades. Both the traits of P. pinaster and the habitat in South Africa are conducive to the success of P. pinaster in this region of the world.

خيارات المكافحة البيولوجية

حشرة and سوس that feed on the seeds and cones of P. pinaster can be effective مكافحة حيوية للآفات options. An insect or mite that acts as an ideal biological control should have a high معدل الخصوبة الكلي and be عائل (أحياء), meaning that it preys specifically on P. pinaster. The دورة حياة (أحياء) of the predator should also match that of its specific host. Two key characteristics the predator should also exhibit are ذاتي الحد and the ability to survive in the presence of a declining prey population.  Seed feeding insects are an effective control because they have high reproductive rates and target the seeds without diminishing the positive effect of the plant on the environment. Controlling the spread of P. pinaster seeds in the region is the key to limiting the growth and spread of this species because P. pinaster has the ability to produce a large number of seeds that are capable of dispersing very efficiently.  One possible option is Trisetacus, an كهربيات (فصيلة) mite. The main advantage to using this mite to control the population of P. Pinaster is its specificity to P. pinaster; it can effectively control the population of P. pinaster by destroying the growing conelets in P. pinaster while limiting its impact to only this species. Another possible option is Pissodes validirostris, a cone-feeding weevil that lays eggs in developing cones. When the يرقة hatch, they feed on the growing seed tissue, preventing P. pinaster seeds from forming and dispersing. Although the adults feed on the trees as well, they do not do any damage to the seeds and only feed on the shoots of the tree, so they do not appear to negatively impact the growth of the trees. Different forms of P. validirostris have diverged to become host-specific to different pine trees. The type of P. validirostris that originated from البرتغال appears to have specialized to P. pinaster; therefore, this insect may be used in the future to control the spread of P. pinaster in South Africa. The uncertainties regarding the host-specificity of different types of P. validirostris, however, require more research to be completed before the introduction of the weevils into South Africa. An introduction of a species that is not host-specific to P. pinaster can lead to detrimental effects on both the environment and صناعة that are dependent on certain tree species.  Two other biological control possibilities include the pyralid moth species Dioryctria mendasella and D. mitatella, but these species attack the vegetative نسيج حيوي instead of just the seeds of P. pinaster, harming the plant itself.  As of now, the eriophyid mite and cone-feeding weevil seem to hold the most potential to controlling the spread of P. pinaster in the regions it has invaded because they destroy the reproductive structures of the target invasive species.