Step-by-Step Guide to Installing Turf in Nevada

Step-by-Step Guide to Installing Turf in Nevada

Synthetic Grass For Side Yards Las Vegas

Choosing the Right Turf Grass for Nevadas Climate


Choosing the right turf grass for Nevadas climate can be a bit of a challenge! Quality Artificial Grass Vegas Nevada. You see, Nevadas got some pretty extreme weather conditions - think sweltering summers and freezing winters. So, you cant just grab any old grass and expect it to thrive.


First things first, you gotta consider the sun. Nevadas got plenty of it! But too much sun can be tough on grass. You want something that can handle the heat without wilting. Bermuda grass is a good choice here. Its tough as nails and loves the sun. Just make sure youve got enough water though, because its a thirsty one!


Then theres the cold. Believe it or not, some parts of Nevada get pretty chilly in the winter. Thats where cool-season grasses come in. Fescues are great for this because they can withstand cold temperatures better than warm-season grasses. But theyre not as drought-tolerant as Bermuda, so you need to be ready to water more often during dry spells.


Now, not everyone wants to water their lawn like crazy. If youre looking for a drought-resistant option that can handle both hot and cold, Blue grama might be for you. Its native to the region and doesn't need much water or maintenance. But its not as lush as other grasses, so it might not be the best choice if you want a super green lawn.


Another thing to keep in mind is soil quality. Synthetic Grass For Side Yards Las Vegas Nevadas not exactly known for its rich, loamy soil. You might have to do some work to improve the soil before planting. Adding compost or other organic matter can help, but its a step you shouldnt skip.


Lastly, dont forget about foot traffic. If youve got kids or pets, youll want a grass that can handle some wear and tear. Bermuda and Fescues are both pretty sturdy, but Blue grama might not be the best choice for high-traffic areas.


In conclusion, choosing the right turf grass for Nevadas climate isn't easy, but its totally doable. You just need to think about the sun, the cold, the water, the soil, and the foot traffic. And hey, if you make a mistake? No worries! You can always try something different next year. Gardening is all about learning and experimenting, right?

Preparing the Soil for Turf Installation


Alright, so youre thinking about laying down some green grass in your yard in Nevada? Well, before you get too excited and start hauling turf, you gotta take a step back and make sure the soils in tip-top shape! You see, preparing the soil is like priming a canvas; without the right base, your turf aint gonna look as lush and healthy as it could.


So, first things first, you gotta clear the area. Get rid of any weeds, rocks, or debris. Its a bit of a pain, but trust me, its worth it. No point in having your new turf grow among old, pesky weeds! Once the areas clean, its time to take a closer look at the soil itself. Check if its loose and aerated. If you push a shovel into the ground and its like trying to dig into concrete, youve got a problem. You need to loosen it up, maybe with a tiller or a garden fork. This helps the roots breathe and spread out.


Dont forget about grading the area. The soil should slope away from buildings and other structures to prevent water from pooling and causing issues. If the areas too flat, water might sit around, leading to root rot. Use a rake or a landscape rake to give it a gentle slope. It doesnt have to be drastic, just enough to ensure proper drainage.


Now, heres the thing: you might not need to add a ton of amendments, but if the soils really sandy or clay-heavy, you might want to consider it. Sand can improve drainage, while clay needs organic matter to loosen it up and improve its structure. Compost is a great option here. It adds nutrients and helps retain moisture. You can spread it out evenly over the soil and mix it in with that garden fork or tiller you used earlier.


Oh, and forget about overwatering the soil. Its tempting to think that more water is better, but thats not the case. Overwatering can lead to compaction and reduce oxygen in the soil, which is bad news for your new turf. Just give it a good soak before you lay down the turf, then let it dry out a bit. This helps the roots establish better when theyre finally in contact with the soil.


So, there you have it. Preparing the soil might seem like a daunting task, but its crucial for the health and longevity of your new turf. Take your time, and dont rush it. Your patience will pay off in the end, I promise!

Laying Out and Installing the Turf Sod


Laying out and installing turf sod is an exciting part of the whole process of creating a beautiful lawn in Nevada. Its not just about rolling out some grass, it's about making sure everythings done right to ensure that your new sod thrives in the dry climate. First things first, you gotta prepare the area where the sod is gonna go. Make sure there's no weeds or debris (you don't want anything competing with your fresh grass!).

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Once the area is prepped, you can start laying out the sod. It's important to stagger the seams, kinda like bricks in a wall, to create a sturdy foundation. You wouldnt want your sod to peel away easily! When you're laying the strips, just unroll them and gently press them down. Its crucial to avoid leaving gaps between the pieces. You dont wanna give those pesky weeds a chance, right?


After youve laid down all the sod, give it a good watering. This step isn't optional! Watering helps to settle the sod into the soil and keeps it from drying out. You might think it's a hassle, but trust me, your lawn will thank you later.


Finally, keep an eye on your new turf for the next few weeks. Don't let it dry out, and avoid heavy foot traffic until it's established. Remember, patience is key! In no time, youll have a lush, green lawn that you can be proud of. What a difference it makes!

Post-Installation Care and Maintenance Tips


After you've gone through the process of installing turf in Nevada, you might think the hard work is over, but that's not entirely true! Post-installation care and maintenance are crucial to ensure your new lawn stays lush and vibrant. So, let's dive into some easy tips to keep your turf looking its best.


First off, watering is a big deal. You've gotta make sure you're giving your turf enough hydration, especially during those hot Nevada summers. It's not just about soaking it for a few minutes; you should aim for a deep watering routine. This helps the roots establish themselves better. But hey, don't go overboard-too much water can lead to problems like mold or even root rot, which you definitely don't want.


Next, let's talk about mowing. You might think turf doesn't need mowing, but that's not true! Regularly trimming the grass helps maintain its height and keeps it looking neat. Just remember to set your mower blade high enough so you're not cutting it too short. Cutting it too low can stress the grass and make it less resilient.


Also, you should keep an eye out for debris. Leaves, twigs, and other stuff can accumulate on your turf, blocking sunlight and trapping moisture.

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A quick cleanup every now and then will prevent any issues, so don't neglect that chore!


Fertilizing is another important aspect of turf care. You'll want to use a quality fertilizer that's appropriate for your grass type and climate. Applying it at the right times will help your turf thrive. Just make sure you're not using too much; that can lead to chemical buildup, which is definitely something you want to avoid.


Lastly, don't forget about the edges! Trimming the borders of your turf not only gives it a polished look but also prevents overgrowth into other areas. Plus, it's a good opportunity to check for any weeds that might be trying to sneak in.


In conclusion, while installing turf in Nevada might seem like the finish line, it's really just the beginning. With some consistent care and attention, your new lawn can stay healthy and beautiful for years to come. So, roll up those sleeves and get to work-you won't regret it!

Featured In

Poly-Turf was a brand of artificial turf in the early 1970s, manufactured by American Biltrite of Wellesley, Massachusetts. It was the first specifically designed for American football, with a patented layered structure which included a "shock pad" between the artificial grass and the asphalt sub-surface.[1] It used polypropylene for its artificial grass blades, rather than the nylon used in AstroTurf and 3M's Tartan Turf.[2][3][4]

History in Miami

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In the late 1960s, the natural grass surface at the Orange Bowl in Miami was constantly in poor condition,[5] primarily due to heavy usage; 34 games were scheduled there during the 1968 football season.[6]

Poly-Turf was installed at the city-owned stadium in 1970,[7] and utilized for six seasons. The stadium was used for both college and professional football, primarily by the University of Miami Hurricanes and the Miami Dolphins of the NFL. It also hosted the eponymous New Year's Day college bowl game, Super Bowl games, and high school football.

The University of Nebraska Cornhuskers won the first three Orange Bowl games played on Poly-Turf, which included two national championships. The first Super Bowl played on artificial turf was played on Poly-Turf in the Orange Bowl in January 1971, when the Baltimore Colts defeated the Dallas Cowboys 16-13 in Super Bowl V. The next Super Bowl at the stadium was the final game played on Poly-Turf in Miami; Super Bowl X in January 1976.[8] Its flaws received additional media exposure the week prior to the game,[9] and Dolphins receiver Nat Moore documented them in a local article.[10]

The longer polypropylene blades of Poly-Turf tended to mat down[11][12] and become very slick under hot & sunny conditions.[13][14][15] Other NFL owners were skeptical of the brand before the first regular season games were played in 1970.[7] The field was replaced after two seasons,[16][17] before the Dolphins' 1972 undefeated season.[18] It was replaced by another Poly-Turf surface. While it had similar problems,[19][20] it lasted longer than the first installation, and was used for four years. Over just six years, both installations deteriorated rapidly and some football players suffered an increasing number of leg and ankle injuries; some players claimed to trip over seams. Prior to the second installation in 1972, the city did not consult with the Dolphins about the replacement; Dolphins' head coach Don Shula preferred a different brand, either AstroTurf or Tartan Turf.[21] The field discolored from green to blue due to the severe UV nature of the Miami sun.[14][22]

Return to natural grass

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The city removed the Poly-Turf in 1976 and re-installed natural grass, a special type known as Prescription Athletic Turf (PAT),[23][24][25] which remained until the stadium's closure in early 2008. As late as December 1975, the city had planned to retain the Poly-Turf for the 1976 season,[23] but that decision was changed a few weeks later, prior to the Super Bowl.[8][26][27]

The Orange Bowl became the first major football venue to replace its artificial turf with natural grass, and it was the third NFL stadium to install Prescription Athletic Turf; Denver's Mile High Stadium and Washington's RFK Stadium installed PAT fields a year earlier in the spring of 1975.[24]

Other installations

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Other NFL stadiums which installed Poly-Turf included Schaefer Stadium, opened in 1971 for the New England Patriots,[11] and Tulane Stadium in New Orleans, home of the Saints, Tulane University, and the Sugar Bowl. Notable college stadiums included Legion Field in Birmingham, Alabama[28] and Alumni Stadium at Boston College.[29]

American Biltrite ceased production of Poly-Turf in 1973; 3M stopped the manufacture of its Tartan Turf in 1974, citing rising oil prices in light of the 1973 oil embargo.[4] This left AstroTurf as the only major manufacturer of artificial turf (with only minor competition along the way) until FieldTurf was introduced in the late 1990s.[30]

References

[edit]
  1. ^ U.S. Patent number 3661687, inventors Arthur F. Spinney and Lawrence J. Warnalis
  2. ^ Underwood, John (November 15, 1971). "New Slant on the Mod Sod". Sports Illustrated. p. 32. Retrieved October 29, 2014.
  3. ^ "Mod-sod revolution felt". Tuscaloosa News. Associated Press. June 30, 1970. p. 8.
  4. ^ a b Johnson, William Oscar (August 12, 1985). "The tyranny of phony fields". Sports Illustrated. p. 34. Retrieved October 29, 2014.
  5. ^ Crittenden, John (October 16, 1968). "Orange Bowl's on the beach". Miami News. p. 1D.
  6. ^ Plaisted, Ed (August 1, 1968). "Orange Bowl grass faces torture test". Miami News. p. 3D.
  7. ^ a b Petrella, Tony (August 30, 1970). "Owners dislike Poly-Turf". Palm Beach Post-Times. p. D4.
  8. ^ a b "It's back to grass for Orange Bowl after Sunday's game". Daytona Beach Morning Journal. Associated Press. January 16, 1976. p. 6B.
  9. ^ "Last-minute repairs". Palm Beach Post-Times. photo. January 17, 1976. p. D1.
  10. ^ Moore, Nat (January 15, 1976). "Dear Sirs". Palm Beach Post. p. D1.
  11. ^ a b "Scorecard: Rug". Sports Illustrated. October 18, 1971. Retrieved October 29, 2014.
  12. ^ "Lazy Miami artificial turf still laying down on job". Eugene Register-Guard. October 20, 1971. p. 3D.
  13. ^ Petrella, Tony (October 5, 1971). "Poly-Turf: a headache". Palm Beach Post. p. D1.
  14. ^ a b Petrella, Tony (October 19, 1971). "Orange Bowl's Poly-Turf: troubles and questions". Palm Beach Post. p. B5.
  15. ^ "Poly-Turf...down or up?". Palm Beach Post. wire services. October 22, 1971. p. H1.
  16. ^ "Biltrite to re-carpet Orange Bowl". Palm Beach Post. January 22, 1972. p. C4.
  17. ^ "Orange Bowl to receive better 'grass'". Palm Beach Daily News. UPI. January 23, 1972. p. 18.
  18. ^ Sun-Sentinel.com – Miami Orange Bowl – 2008
  19. ^ Nobles, Charlie (September 6, 1972). "Slippery turf infuriates Hurricanes". Miami News. p. 1D.
  20. ^ Treglown, Dick (September 26, 1972). "Orange Bowl turf: a slippery subject". Palm Beach Post. p. C1.
  21. ^ "OB Poly-Turf: A mean green". Evening Independent. St. Petersburg, Florida. Associated Press. September 26, 1972. p. 1C.
  22. ^ MiamiSouthpaw.blogspot.com – "Ghosts of Orange Bowl Poly-Turf" – 2009-08
  23. ^ a b "Orange Bowl sticks with Poly-Turf". Miami News. December 20, 1975. p. 2B.
  24. ^ a b Nobles, Charlie (January 28, 1976). "PAT can be used to soften visitors". Miami News. p. 1C.
  25. ^ Nobles, Charlie (July 31, 1976). "Dolphins find fewer bugs without rug as Vikings visit". Miami News. p. 1B.
  26. ^ Nobles, Charlie (February 10, 1976). "Orange Bowl will install grass". Miami News. p. 1C.
  27. ^ "Orange Bowl taking out Poly Turf". Lawrence Journal World. Kansas. February 14, 1976. p. 17.
  28. ^ "Poly-Turf for Legion". The Tuscaloosa News. Associated Press. May 19, 1970. p. 7. Retrieved January 20, 2014.
  29. ^ Reid, Jan (December 1979). "The real mean green". Texas Monthly. p. 153.
  30. ^ "Living with Artificial Grass" American Journal of Sports Medicine vol. 18, no. 4, 1990-07

 

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Energy-efficient landscaping is a type of landscaping designed for the purpose of conserving energy. There is a distinction between the embedded energy of materials and constructing the landscape, and the energy consumed by the maintenance and operations of a landscape.

Terminology and definition

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Landscaping often refers to the practice of landscape design and gardening, which traditionally concern with designing sites with vegetation and craft for aesthetic, cultural, social, and religious purposes.

Landscape architecture and landscape engineering, on the other hand, are multi-disciplinary and interdisciplinary professions that integrate technical considerations, such as geography, ecology, biology, and engineering, into the design of landscape and the actualization of it.

Energy-efficient landscaping falls into the categories of the latter, and it stresses the energy conservation in site operation or the creation of the site. Among its various term usage, energy-efficient landscaping can refer to the reduction of energy usage in maintenance and operation of the landscape narrowly for the user/owner of the site,[1][2] or broadly for the energy conservation of the global environment, such as mitigating urban heat island effect with reflective surface (increase albedo) or reducing the need of water treatment and sewage by using pervious pavement. Common methods of energy-efficient landscaping include reducing heat or cooling load of a building through shade, wind-blocking, and insulation; management of water; and using plants or construction material that cost less energy.

Methods and techniques

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Design techniques include:

Shade with trees

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Planting trees for the purpose of providing shade, which reduces cooling costs. The mature height of the trees and their canopy shape need to be well studied. The locations of the trees should be chosen based on their height and the height of the building. Also, when trees are planted closer to the windows or walls, they will provide shade for a greater portion of the day as the Sun keep changing its relative position to the window and the trees. Planting the trees too close to the building, however, is also not desirable, as it might create the danger of touching above-ground or underground utility lines.[2]

The type of leaves of the trees is also important. Broad-leaf evergreens like Southern magnolia can be used to provide dense year-round shade. However, needle-leaf evergreens like pines and cedars can provide more air circulation though their shade is sparser and more open.[2]

Not only can tree shade be used to reduce the cooling load in building, it can also be used in parking lot, driveways, and playgrounds.[3]

Windbreak

[edit]

Planting or building windbreaks to slow winds near buildings, which reduces heat loss. Homes loses heat through infiltration in the Winter. Windbreaks should be designed to intercept and redirect the Winter winds before they reach the house and outdoor areas with playgrounds or sensitive plants. The windbreak in the Winter should also be designed so that they would not block the sunlight in the Winter or block the wind in the Summer.[3]

Wall sheltering with shrubbery or vines

[edit]

Planting shrubs near the wall creates an insulating air space around the wall. This is a similar idea to the use of a tree windbreak. Shrubs should be planted at least 2 feet (0.61 m) from the wall to prevent moisture and insect problems.[2]

Taking advantage of natural landform

[edit]

Earth sheltering is an example of using natural landform and geological condition to save energy in building a structure. It is believed to save energy in multiple ways: by using the rock or strong

An Earth house by Peter Vetsch

soil as wall and ground as the floor, construction cost is greatly reduced, because the structure will need less load bearing material and there is no need for excavation and foundation construction; the wall and the floor made of natural material likely will have better insulation than artificial wall and floors; Natural walls and floors can also reduce fire hazard, because they are hard to be ignited thus reduce the need for flame retardants.[4]

In a study of simulating a structure with varying depth submerged in the ground to understand the insulating effect of natural wall and ground in cold climate,[5] it was found that the thermal transmittance of the earth-sheltered walls and floor is 16% - 45% lower than that of the structure totally above ground.

Other than Earth Sheltering, a simpler way of taking advantage of natural landform is using geology, such as mountains, for shade.

Green roofs

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Often, landscape design and architecture refers to the design in ground surface; in many contexts, specifically, the design guidance and topics are for a typical residential landscape in suburban housing, where there is a yard (garden), a driveway, and a house. In the crowded urban area, however, there is not abundant ground surface for landscape design. Green roofs, then, become an appealing option to add some aesthetics and green to the crowded cities. Not limited to the cities, green roofs can be applied to wherever it will fit. Most of times, actually, the decision to build Green roofs is based on local climate and policy. It is because other than its aesthetics, green roofs are used often for their ability to conserve energy, such as increasing insulation of the building roof, retaining and infiltrating rainwater, and potentially reducing urban heat island effect when it was installed to a certain scale. In Germany, for example, partly because of EU's regulation, 17% of the new roof construction are green roofs. In Washington DC, green roofs are used as an alternative storm-water retention technique.[6]

Chicago City Hall Green Roof

Benefits

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Reducing building energy consumption by increasing the roof insulation: In total energy consumption reduction, green roof would have the best performance relative to a bare roof in a colder climate, which require nighttime heating. The reduction in heating load of the building increase as the soil depth of the green roof increase, though an increased soil depth would mean heavier roof. On the other hand, if a building is cooling-dominated, leaf area index is more important. In peak energy consumption reduction, green roof also has a notable effect, and the leaf area index and soil depth are both positively related to its performance.[7]

Rainwater retention and evapotranspiration: 3-4 inches of soil can retain about 1 inch of rainwater. That is about 75% of precipitation in most areas in United States.[8] By retaining the rainwater in soil, the water would not become runoff, instead they would result in evapotranspiration.

Controversies

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Water runoff quality: When green roof is not able to hold the amount of the precipitation, the excessive rainwater will become runoff. In a field experiment where contaminated water is dripped into a green roof section to mimic rainfall in the green roof, the exfiltrate water was studied and analyzed. It was found that since the average level of suspended solid, nitrogen, and phosphorus concentrations in Green roof water outflow is significantly higher than that in conventional roof outflow, extensive green roofs will become a source of nutrient contamination in urban water environment.[9]

Fire Hazard: Green roofs can be more easily ignited than conventional roofs; it is a concern that when the green roof caught fire, the high temperature would damage the roof structure itself. Not only the idea of damaging the roof is contradictory to energy conservation and sustainability, the fire and the roof damage could cause safety issue to the residents. It remains a matter of debate as to whether a green roof will exacerbate or mitigate the effects of a fire. Some argue that, because vegetation is about 95% water, the green roof actually reduces chances of a fire. On the other hand, some argue that during autumn and winter, when the vegetation is dry, fire hazard is increased. A recent study has found, through mathematical modelling, that [10] when the vegetation itself caught fire, heat does penetrate downward (rather slowly as the thermal conductivity of soil is low), eventually damaging the roof itself. Thus the key to whether ignited vegetation will damage the roof or not depends on the thickness of the soil. The study also found that by installing a gypsum layer beneath the soil layer, the possibility of damaging the roof can be greatly reduced.

Additional structural load: Most old buildings were not designed for the extra roof dead load of the green roofs. If more energy is consumed in building the additional load bearing structure for the green roofs than the energy saved through insulation enhancement and water retention, it would be contradictory to the idea of energy conservation. By study, common green roofs types in the market would increase the load on the rood by 1.2 to 2.43 kilo-newton per square meter.[11]

Pervious (porous/permeable) paving

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A lot pavement in urban and suburban areas is impervious, this likely would result the contaminated stormwater runoff. In pre-development area, averagely 50% of storm-water would result in evapotranspiration, 5% in runoff, and 45% in infiltration, whereas in post-development area, only 35% storm-water result in evapotranspiration, and 50% in runoff, and 15% in infiltration. This change has caused various problem, such as flooding, infrastructural damage due to rapid movement of water, and water contamination.[12]

By using pervious paving, however, the amount of infiltrated storm-water will be increased in post-development area, and the pollutants in the filtrated water can be reduced; thus the problem can be mitigated. In Low Impact Development 2008 Conference, ASCE performed two bench-scale study to examine the effectiveness of permeable interlocking concrete pavement in terms of water flow rate and the role of microbial colonies in pollutant removal in the micro-environment of porous pavement.[13] The experiment shows 84% relative total suspended solids (TSS) removal on average, yet the increased relative removal over time suggests there is potentially solid buildup, and that may result system clogging and system failure. The evidence in pollutant removal proved the conclusion of the previous study that the annual pollutant runoff from the driveways was 86% lower for pervious driveways than impervious driveways.

Types of Pervious pavement include:[12]

Porous asphalt

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Advantage: Relatively low cost; Easy access to the material; Workers are experienced with it

Disadvantage: Susceptible to water damage; Usually used for short-term only; Low relative strength

Pervious concrete

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Advantage: High structural strength; Easy access to the material

Disadvantage: Slow construction process; High initial cost

Permeable interlocking concrete paver

[edit]

Advantage: Ease of Construction, Aesthetics, Ease of maintenance and repair

Disadvantage: High Cost; Only can be used for low speed road way

Grid Pavement

Grid pavement

[edit]

Advantage: Wide variety of products; Relatively inexpensive; Ease of maintenance and repair

Disadvantage: Typically limited to parking areas

The decision among different permeable pavement types depends on the need of the project, available material and equipment, and budget.

Effective and smart lighting

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Site lighting with full cut off fixtures, light level sensors, and high efficiency fixtures.

Structure orientation

[edit]

The sun rises from the East, moves South, and sets in the West. Thus, a rule of thumb for design is to avoid south-facing windows when trying to decrease cooling load of the building and increase south-facing windows when trying to decrease heating load of the building. The reality, however, is more complicated. The sun rises from East and sets in West perfectly only on the autumnal and vernal equinoxes, and during the vast majority of the year, Sun travels slightly southward and eastward depending on whether it is summer or winter and on whether the observer is in the Northern Hemisphere or the Southern Hemisphere.[14]

To design for the best performance of the site, the designer needs to well understand the local climate and the site's location relative to equator.

More to include

[edit]

Energy-efficient landscaping techniques include using local materials, on-site composting and chipping to reduce green waste hauling, hand tools instead of gasoline-powered, and also may involve using drought-resistant plantings in arid areas, buying stock from local growers to avoid energy in transportation, and similar techniques.

Example

[edit]

In agreement with the city to build a resilient and sustainable landscape, Massachusetts Institute of Technology has initiated several energy efficiency upgrade projects, these projects include:

  • Planting trees and using the tree canopy to provide shade for pedestrians, which also would give students more incentive to walk
  • Landscape filters are added to (partly) treat rain water
  • Storm-water storage are installed to mitigate flood
  • Lighter color pavement for reducing heat island effect

See also

[edit]
[edit]

References

[edit]
  1. ^ Mansfield, Robyn (1996). "Energy efficient landscaping". Soft Technology: Alternative Technology in Australia (56): 24–25. ISSN 0810-1434.
  2. ^ a b c d DelValle, Terry B.; Bradshaw, Joan; Larson, Barbra; Ruppert, Kathleen C. (2008-07-09). "Energy Efficient Homes: Landscaping: FCS3281/FY1050, 6/2008". EDIS. 2008 (5). doi:10.32473/edis-fy1050-2008. ISSN 2576-0009. S2CID 245098464.
  3. ^ a b Hoeven, Gustaaf A. van der (November 1982). "Energy efficient landscaping". cite journal: Cite journal requires |journal= (help)
  4. ^ "Earth-sheltered houses". Lowimpact.org. Retrieved 2021-12-15.[permanent dead link]
  5. ^ Berezin, D V (2019-12-01). "Earth-sheltering effect on dwelling in cold climate: simulation-based and theoretical approaches". IOP Conference Series: Materials Science and Engineering. 687 (5): 055042. Bibcode:2019MS&E..687e5042B. doi:10.1088/1757-899x/687/5/055042. ISSN 1757-8981. S2CID 213946214.
  6. ^ Celik, Serdar; Morgan, Susan; Retzlaff, William A. (April 2010). "Energy Conservation Analysis of Various Green Roof Systems". 2010 IEEE Green Technologies Conference. pp. 1–4. doi:10.1109/GREEN.2010.5453802. ISBN 978-1-4244-5274-3. S2CID 23090814.
  7. ^ Sailor, David J.; Elley, Timothy B.; Gibson, Max (2011-09-13). "Exploring the building energy impacts of green roof design decisions – a modeling study of buildings in four distinct climates". Journal of Building Physics. 35 (4): 372–391. doi:10.1177/1744259111420076. ISSN 1744-2591. S2CID 108512300.
  8. ^ Johnson, Peter (Sep 2008). "Green Roof Performance Measures" (PDF).
  9. ^ Liu, Wen; Wei, Wei; Chen, Weiping; Deo, Ravinesh C.; Si, Jianhua; Xi, Haiyang; Li, Baofeng; Feng, Qi (September 2019). "The impacts of substrate and vegetation on stormwater runoff quality from extensive green roofs". Journal of Hydrology. 576: 575–582. Bibcode:2019JHyd..576..575L. doi:10.1016/j.jhydrol.2019.06.061. ISSN 0022-1694. S2CID 197576248.
  10. ^ Gerzhova; Blanchet; Dagenais; Côté; Ménard (2019-09-19). "Heat Transfer Behavior of Green Roof Systems Under Fire Condition: A Numerical Study". Buildings. 9 (9): 206. doi:10.3390/buildings9090206. hdl:20.500.11794/66393. ISSN 2075-5309.
  11. ^ Cascone, Stefano; Catania, Federico; Gagliano, Antonio; Sciuto, Gaetano (May 2018). "A comprehensive study on green roof performance for retrofitting existing buildings". Building and Environment. 136: 227–239. Bibcode:2018BuEnv.136..227C. doi:10.1016/j.buildenv.2018.03.052. ISSN 0360-1323.
  12. ^ a b "Permeable Pavements" (PDF). Pervious Pavement.
  13. ^ Rowe, Amy A.; Borst, Michael; O'Connor, Thomas P. (2012-04-26). "Pervious Pavement System Evaluation". Low Impact Development for Urban Ecosystem and Habitat Protection. pp. 1–9. doi:10.1061/41009(333)25. ISBN 9780784410097.
  14. ^ "Building Orientation for Optimum Energy". www.nachi.org. Retrieved 2021-12-16.

 

Land cover surrounding Madison, Wisconsin. Fields are colored yellow and brown and urban surfaces are colored red.
Impervious surfaces surrounding Madison, Wisconsin
Canopy cover surrounding Madison, Wisconsin

Landscape ecology is the science of studying and improving relationships between ecological processes in the environment and particular ecosystems. This is done within a variety of landscape scales, development spatial patterns, and organizational levels of research and policy.[1][2][3] Landscape ecology can be described as the science of "landscape diversity" as the synergetic result of biodiversity and geodiversity.[4]

As a highly interdisciplinary field in systems science, landscape ecology integrates biophysical and analytical approaches with humanistic and holistic perspectives across the natural sciences and social sciences. Landscapes are spatially heterogeneous geographic areas characterized by diverse interacting patches or ecosystems, ranging from relatively natural terrestrial and aquatic systems such as forests, grasslands, and lakes to human-dominated environments including agricultural and urban settings.[2][5][6]

The most salient characteristics of landscape ecology are its emphasis on the relationship among pattern, process and scales, and its focus on broad-scale ecological and environmental issues. These necessitate the coupling between biophysical and socioeconomic sciences. Key research topics in landscape ecology include ecological flows in landscape mosaics, land use and land cover change, scaling, relating landscape pattern analysis with ecological processes, and landscape conservation and sustainability.[7] Landscape ecology also studies the role of human impacts on landscape diversity in the development and spreading of new human pathogens that could trigger epidemics.[8][9]

Terminology

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The German term Landschaftsökologie – thus landscape ecology – was coined by German geographer Carl Troll in 1939.[10] He developed this terminology and many early concepts of landscape ecology as part of his early work, which consisted of applying aerial photograph interpretation to studies of interactions between environment and vegetation.

Explanation

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Heterogeneity is the measure of how parts of a landscape differ from one another. Landscape ecology looks at how this spatial structure affects organism abundance at the landscape level, as well as the behavior and functioning of the landscape as a whole. This includes studying the influence of pattern, or the internal order of a landscape, on process, or the continuous operation of functions of organisms.[11] Landscape ecology also includes geomorphology as applied to the design and architecture of landscapes.[12] Geomorphology is the study of how geological formations are responsible for the structure of a landscape.

History

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Evolution of theory

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One central landscape ecology theory originated from MacArthur & Wilson's The Theory of Island Biogeography. This work considered the biodiversity on islands as the result of competing forces of colonization from a mainland stock and stochastic extinction. The concepts of island biogeography were generalized from physical islands to abstract patches of habitat by Levins' metapopulation model (which can be applied e.g. to forest islands in the agricultural landscape[13]). This generalization spurred the growth of landscape ecology by providing conservation biologists a new tool to assess how habitat fragmentation affects population viability. Recent growth of landscape ecology owes much to the development of geographic information systems (GIS)[14] and the availability of large-extent habitat data (e.g. remotely sensed datasets).

Development as a discipline

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Landscape ecology developed in Europe from historical planning on human-dominated landscapes. Concepts from general ecology theory were integrated in North America.[when?] While general ecology theory and its sub-disciplines focused on the study of more homogenous, discrete community units organized in a hierarchical structure (typically as ecosystems, populations, species, and communities), landscape ecology built upon heterogeneity in space and time. It frequently included human-caused landscape changes in theory and application of concepts.[15]

By 1980, landscape ecology was a discrete, established discipline. It was marked by the organization of the International Association for Landscape Ecology (IALE) in 1982. Landmark book publications defined the scope and goals of the discipline, including Naveh and Lieberman[16] and Forman and Godron.[17][18] Forman[6] wrote that although study of "the ecology of spatial configuration at the human scale" was barely a decade old, there was strong potential for theory development and application of the conceptual framework.

Today, theory and application of landscape ecology continues to develop through a need for innovative applications in a changing landscape and environment. Landscape ecology relies on advanced technologies such as remote sensing, GIS, and models. There has been associated development of powerful quantitative methods to examine the interactions of patterns and processes.[5] An example would be determining the amount of carbon present in the soil based on landform over a landscape, derived from GIS maps, vegetation types, and rainfall data for a region. Remote sensing work has been used to extend landscape ecology to the field of predictive vegetation mapping, for instance by Janet Franklin.

Definitions/conceptions of landscape ecology

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Nowadays, at least six different conceptions of landscape ecology can be identified: one group tending toward the more disciplinary concept of ecology (subdiscipline of biology; in conceptions 2, 3, and 4) and another group—characterized by the interdisciplinary study of relations between human societies and their environment—inclined toward the integrated view of geography (in conceptions 1, 5, and 6):[19]

  1. Interdisciplinary analysis of subjectively defined landscape units (e.g. Neef School[20][21]): Landscapes are defined in terms of uniformity in land use. Landscape ecology explores the landscape's natural potential in terms of functional utility for human societies. To analyse this potential, it is necessary to draw on several natural sciences.
  2. Topological ecology at the landscape scale[22][23] 'Landscape' is defined as a heterogeneous land area composed of a cluster of interacting ecosystems (woods, meadows, marshes, villages, etc.) that is repeated in similar form throughout. It is explicitly stated that landscapes are areas at a kilometres wide human scale of perception, modification, etc. Landscape ecology describes and explains the landscapes' characteristic patterns of ecosystems and investigates the flux of energy, mineral nutrients, and species among their component ecosystems, providing important knowledge for addressing land-use issues.
  3. Organism-centered, multi-scale topological ecology (e.g. John A. Wiens[24][25]): Explicitly rejecting views expounded by Troll, Zonneveld, Naveh, Forman & Godron, etc., landscape and landscape ecology are defined independently of human perceptions, interests, and modifications of nature. 'Landscape' is defined – regardless of scale – as the 'template' on which spatial patterns influence ecological processes. Not humans, but rather the respective species being studied is the point of reference for what constitutes a landscape.
  4. Topological ecology at the landscape level of biological organisation (e.g. Urban et al.[26]): On the basis of ecological hierarchy theory, it is presupposed that nature is working at multiple scales and has different levels of organisation which are part of a rate-structured, nested hierarchy. Specifically, it is claimed that, above the ecosystem level, a landscape level exists which is generated and identifiable by high interaction intensity between ecosystems, a specific interaction frequency and, typically, a corresponding spatial scale. Landscape ecology is defined as ecology that focuses on the influence exerted by spatial and temporal patterns on the organisation of, and interaction among, functionally integrated multispecies ecosystems.
  5. Analysis of social-ecological systems using the natural and social sciences and humanities (e.g. Leser;[27] Naveh;[28][29] Zonneveld[30]): Landscape ecology is defined as an interdisciplinary super-science that explores the relationship between human societies and their specific environment, making use of not only various natural sciences, but also social sciences and humanities. This conception is grounded in the assumption that social systems are linked to their specific ambient ecological system in such a way that both systems together form a co-evolutionary, self-organising unity called 'landscape'. Societies' cultural, social and economic dimensions are regarded as an integral part of the global ecological hierarchy, and landscapes are claimed to be the manifest systems of the 'total human ecosystem' (Naveh) which encompasses both the physical ('geospheric') and mental ('noospheric') spheres.
  6. Ecology guided by cultural meanings of lifeworldly landscapes (frequently pursued in practice[31] but not defined, but see, e.g., Hard;[32] Trepl[19]): Landscape ecology is defined as ecology that is guided by an external aim, namely, to maintain and develop lifeworldly landscapes. It provides the ecological knowledge necessary to achieve these goals. It investigates how to sustain and develop those populations and ecosystems which (i) are the material 'vehicles' of lifeworldly, aesthetic and symbolic landscapes and, at the same time, (ii) meet societies' functional requirements, including provisioning, regulating, and supporting ecosystem services. Thus landscape ecology is concerned mainly with the populations and ecosystems which have resulted from traditional, regionally specific forms of land use.

Relationship to ecological theory

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Some research programmes of landscape ecology theory, namely those standing in the European tradition, may be slightly outside of the "classical and preferred domain of scientific disciplines" because of the large, heterogeneous areas of study. However, general ecology theory is central to landscape ecology theory in many aspects. Landscape ecology consists of four main principles: the development and dynamics of spatial heterogeneity, interactions and exchanges across heterogeneous landscapes, influences of spatial heterogeneity on biotic and abiotic processes, and the management of spatial heterogeneity. The main difference from traditional ecological studies, which frequently assume that systems are spatially homogenous, is the consideration of spatial patterns.[33]

Important terms

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Landscape ecology not only created new terms, but also incorporated existing ecological terms in new ways. Many of the terms used in landscape ecology are as interconnected and interrelated as the discipline itself.

Landscape

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Certainly, 'landscape' is a central concept in landscape ecology. It is, however, defined in quite different ways. For example:[19] Carl Troll conceives of landscape not as a mental construct but as an objectively given 'organic entity', a harmonic individuum of space.[34] Ernst Neef[20][21] defines landscapes as sections within the uninterrupted earth-wide interconnection of geofactors which are defined as such on the basis of their uniformity in terms of a specific land use, and are thus defined in an anthropocentric and relativistic way. According to Richard Forman and Michel Godron,[22] a landscape is a heterogeneous land area composed of a cluster of interacting ecosystems that is repeated in similar form throughout, whereby they list woods, meadows, marshes and villages as examples of a landscape's ecosystems, and state that a landscape is an area at least a few kilometres wide. John A. Wiens[24][25] opposes the traditional view expounded by Carl Troll, Isaak S. Zonneveld, Zev Naveh, Richard T. T. Forman/Michel Godron and others that landscapes are arenas in which humans interact with their environments on a kilometre-wide scale; instead, he defines 'landscape'—regardless of scale—as "the template on which spatial patterns influence ecological processes".[25][35] Some define 'landscape' as an area containing two or more ecosystems in close proximity.[15]

Scale and heterogeneity (incorporating composition, structure, and function)

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A main concept in landscape ecology is scale. Scale represents the real world as translated onto a map, relating distance on a map image and the corresponding distance on earth.[36] Scale is also the spatial or temporal measure of an object or a process,[33] or amount of spatial resolution.[6] Components of scale include composition, structure, and function, which are all important ecological concepts. Applied to landscape ecology, composition refers to the number of patch types (see below) represented on a landscape and their relative abundance. For example, the amount of forest or wetland, the length of forest edge, or the density of roads can be aspects of landscape composition. Structure is determined by the composition, the configuration, and the proportion of different patches across the landscape, while function refers to how each element in the landscape interacts based on its life cycle events.[33] Pattern is the term for the contents and internal order of a heterogeneous area of land.[17]

A landscape with structure and pattern implies that it has spatial heterogeneity, or the uneven distribution of objects across the landscape.[6] Heterogeneity is a key element of landscape ecology that separates this discipline from other branches of ecology. Landscape heterogeneity is able to quantify with agent-based methods as well.[37]

Patch and mosaic

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Patch, a term fundamental to landscape ecology, is defined as a relatively homogeneous area that differs from its surroundings.[6] Patches are the basic unit of the landscape that change and fluctuate, a process called patch dynamics. Patches have a definite shape and spatial configuration, and can be described compositionally by internal variables such as number of trees, number of tree species, height of trees, or other similar measurements.[6]

Matrix is the "background ecological system" of a landscape with a high degree of connectivity. Connectivity is the measure of how connected or spatially continuous a corridor, network, or matrix is.[6] For example, a forested landscape (matrix) with fewer gaps in forest cover (open patches) will have higher connectivity. Corridors have important functions as strips of a particular type of landscape differing from adjacent land on both sides.[6] A network is an interconnected system of corridors while mosaic describes the pattern of patches, corridors, and matrix that form a landscape in its entirety.[6]

Boundary and edge

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Landscape patches have a boundary between them which can be defined or fuzzy.[15] The zone composed of the edges of adjacent ecosystems is the boundary.[6] Edge means the portion of an ecosystem near its perimeter, where influences of the adjacent patches can cause an environmental difference between the interior of the patch and its edge. This edge effect includes a distinctive species composition or abundance.[6] For example, when a landscape is a mosaic of perceptibly different types, such as a forest adjacent to a grassland, the edge is the location where the two types adjoin. In a continuous landscape, such as a forest giving way to open woodland, the exact edge location is fuzzy and is sometimes determined by a local gradient exceeding a threshold, such as the point where the tree cover falls below thirty-five percent.[33]

Ecotones, ecoclines, and ecotopes

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A type of boundary is the ecotone, or the transitional zone between two communities.[12] Ecotones can arise naturally, such as a lakeshore, or can be human-created, such as a cleared agricultural field from a forest.[12] The ecotonal community retains characteristics of each bordering community and often contains species not found in the adjacent communities. Classic examples of ecotones include fencerows, forest to marshlands transitions, forest to grassland transitions, or land-water interfaces such as riparian zones in forests. Characteristics of ecotones include vegetational sharpness, physiognomic change, occurrence of a spatial community mosaic, many exotic species, ecotonal species, spatial mass effect, and species richness higher or lower than either side of the ecotone.[38]

An ecocline is another type of landscape boundary, but it is a gradual and continuous change in environmental conditions of an ecosystem or community. Ecoclines help explain the distribution and diversity of organisms within a landscape because certain organisms survive better under certain conditions, which change along the ecocline. They contain heterogeneous communities which are considered more environmentally stable than those of ecotones.[39] An ecotope is a spatial term representing the smallest ecologically distinct unit in mapping and classification of landscapes.[6] Relatively homogeneous, they are spatially explicit landscape units used to stratify landscapes into ecologically distinct features. They are useful for the measurement and mapping of landscape structure, function, and change over time, and to examine the effects of disturbance and fragmentation.

Disturbance and fragmentation

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Disturbance is an event that significantly alters the pattern of variation in the structure or function of a system. Fragmentation is the breaking up of a habitat, ecosystem, or land-use type into smaller parcels.[6] Disturbance is generally considered a natural process. Fragmentation causes land transformation, an important process in landscapes as development occurs.

An important consequence of repeated, random clearing (whether by natural disturbance or human activity) is that contiguous cover can break down into isolated patches. This happens when the area cleared exceeds a critical level, which means that landscapes exhibit two phases: connected and disconnected.[40]

Theory

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Landscape ecology theory stresses the role of human impacts on landscape structures and functions. It also proposes ways for restoring degraded landscapes.[16] Landscape ecology explicitly includes humans as entities that cause functional changes on the landscape.[15] Landscape ecology theory includes the landscape stability principle, which emphasizes the importance of landscape structural heterogeneity in developing resistance to disturbances, recovery from disturbances, and promoting total system stability.[17] This principle is a major contribution to general ecological theories which highlight the importance of relationships among the various components of the landscape.

Integrity of landscape components helps maintain resistance to external threats, including development and land transformation by human activity.[5] Analysis of land use change has included a strongly geographical approach which has led to the acceptance of the idea of multifunctional properties of landscapes.[18] There are still calls for a more unified theory of landscape ecology due to differences in professional opinion among ecologists and its interdisciplinary approach (Bastian 2001).

An important related theory is hierarchy theory, which refers to how systems of discrete functional elements operate when linked at two or more scales. For example, a forested landscape might be hierarchically composed of drainage basins, which in turn are composed of local ecosystems, which are in turn composed of individual trees and gaps.[6] Recent theoretical developments in landscape ecology have emphasized the relationship between pattern and process, as well as the effect that changes in spatial scale has on the potential to extrapolate information across scales.[33] Several studies suggest that the landscape has critical thresholds at which ecological processes will show dramatic changes, such as the complete transformation of a landscape by an invasive species due to small changes in temperature characteristics which favor the invasive's habitat requirements.[33]

Application

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Research directions

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Developments in landscape ecology illustrate the important relationships between spatial patterns and ecological processes. These developments incorporate quantitative methods that link spatial patterns and ecological processes at broad spatial and temporal scales. This linkage of time, space, and environmental change can assist managers in applying plans to solve environmental problems.[5] The increased attention in recent years on spatial dynamics has highlighted the need for new quantitative methods that can analyze patterns, determine the importance of spatially explicit processes, and develop reliable models.[33] Multivariate analysis techniques are frequently used to examine landscape level vegetation patterns. Studies use statistical techniques, such as cluster analysis, canonical correspondence analysis (CCA), or detrended correspondence analysis (DCA), for classifying vegetation. Gradient analysis is another way to determine the vegetation structure across a landscape or to help delineate critical wetland habitat for conservation or mitigation purposes (Choesin and Boerner 2002).[41]

Climate change is another major component in structuring current research in landscape ecology.[42] Ecotones, as a basic unit in landscape studies, may have significance for management under climate change scenarios, since change effects are likely to be seen at ecotones first because of the unstable nature of a fringe habitat.[38] Research in northern regions has examined landscape ecological processes, such as the accumulation of snow, melting, freeze-thaw action, percolation, soil moisture variation, and temperature regimes through long-term measurements in Norway.[43] The study analyzes gradients across space and time between ecosystems of the central high mountains to determine relationships between distribution patterns of animals in their environment. Looking at where animals live, and how vegetation shifts over time, may provide insight into changes in snow and ice over long periods of time across the landscape as a whole.

Other landscape-scale studies maintain that human impact is likely the main determinant of landscape pattern over much of the globe.[44][45] Landscapes may become substitutes for biodiversity measures because plant and animal composition differs between samples taken from sites within different landscape categories. Taxa, or different species, can "leak" from one habitat into another, which has implications for landscape ecology. As human land use practices expand and continue to increase the proportion of edges in landscapes, the effects of this leakage across edges on assemblage integrity may become more significant in conservation. This is because taxa may be conserved across landscape levels, if not at local levels.[46]

Land change modeling

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Land change modeling is an application of landscape ecology designed to predict future changes in land use. Land change models are used in urban planning, geography, GIS, and other disciplines to gain a clear understanding of the course of a landscape.[47] In recent years, much of the Earth's land cover has changed rapidly, whether from deforestation or the expansion of urban areas.[48]

Relationship to other disciplines

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Landscape ecology has been incorporated into a variety of ecological subdisciplines. For example, it is closely linked to land change science, the interdisciplinary of land use and land cover change and their effects on surrounding ecology. Another recent development has been the more explicit consideration of spatial concepts and principles applied to the study of lakes, streams, and wetlands in the field of landscape limnology. Seascape ecology is a marine and coastal application of landscape ecology.[49] In addition, landscape ecology has important links to application-oriented disciplines such as agriculture and forestry. In agriculture, landscape ecology has introduced new options for the management of environmental threats brought about by the intensification of agricultural practices. Agriculture has always been a strong human impact on ecosystems.[18]

In forestry, from structuring stands for fuelwood and timber to ordering stands across landscapes to enhance aesthetics, consumer needs have affected conservation and use of forested landscapes. Landscape forestry provides methods, concepts, and analytic procedures for landscape forestry.[50] Landscape ecology has been cited as a contributor to the development of fisheries biology as a distinct biological science discipline,[51] and is frequently incorporated in study design for wetland delineation in hydrology.[39] It has helped shape integrated landscape management.[52] Lastly, landscape ecology has been very influential for progressing sustainability science and sustainable development planning. For example, a recent study assessed sustainable urbanization across Europe using evaluation indices, country-landscapes, and landscape ecology tools and methods.[53]

Landscape ecology has also been combined with population genetics to form the field of landscape genetics, which addresses how landscape features influence the population structure and gene flow of plant and animal populations across space and time[54] and on how the quality of intervening landscape, known as "matrix", influences spatial variation.[55] After the term was coined in 2003, the field of landscape genetics had expanded to over 655 studies by 2010,[56] and continues to grow today. As genetic data has become more readily accessible, it is increasingly being used by ecologists to answer novel evolutionary and ecological questions,[57] many with regard to how landscapes effect evolutionary processes, especially in human-modified landscapes, which are experiencing biodiversity loss.[58]

See also

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References

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[edit]

 

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Reviews for Rock N Block - Turf N Hardscapes


Rock N Block - Turf N Hardscapes

Dawna OgleYohe

(5)

My initial contact was with Ray, whom did an excellent job giving me an estimate on what I wanted done in my small yard and walkway., the guys that came out and did the work were superior. They did an excellent job. I’m very pleased with this company. I will highly recommend them to family and friends, and I will be using them in the near future for other little projects.

Rock N Block - Turf N Hardscapes

Josh Bodell

(5)

Eric and team did an amazing job. They worked with me for months while I got HOA approval for the project. Once they began working they were great, going over everything in detail and making sure things were perfect. This project included wall repair, stucco and paint repair, paver and turf installation. Extremely satisfied with this experience.

Rock N Block - Turf N Hardscapes

John Picard

(5)

Above and beyond. I’ve got 20 years in the construction industry and these guys are top notch. Tell them what you need, they’ll work with you. Communication is clear and they want to make you feel good about the whole process: If I had to do our back yard 100 more times I’d use rock n block every time. The owner is a stand up man, his project managers, even down to his workers. All respectful, hard working people. This is a call you won’t regret making.

Rock N Block - Turf N Hardscapes

Randy Blair

(5)

I had turf and a sidewalk of pavers put down. Wes was amazing and got me all hooked up with a plan and had tons of options for me to choose from. He handled everything. After we got locked in the crew showed up a few weeks later and the went to work like animals. Those guys killed it. Everything looks amazing. I plan to call Wes back when I'm ready for my next project in the front of the yard. Thank you Wes and everyone who killed this project

Rock N Block - Turf N Hardscapes

Rob Foster

(5)

We have been working with Al and the team for many years (8) to be exact. We have had the pleasure of working with many of their clients throughout this time and we absolutely love how their clients are so pleased with the work they do and the outcome of the projects! The sales team and staff have been very supportive and professional and that’s hard to come by. We look forward to many more years of this partnership with a very positive and motivated company that’s always looking out for the best interests of the community!

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Frequently Asked Questions

Absolutely! Artificial grass is ideal for Las Vegas due to its extreme heat and water restrictions. It stays green year-round without the need for constant watering or mowing. It also holds up well against UV rays, making it a durable and eco-friendly alternative to natural grass in desert environments

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With proper installation and minimal maintenance, artificial grass in Las Vegas can last 15–20 years. The synthetic turf is designed to withstand high temperatures, intense sun exposure, and heavy foot traffic—making it a long-lasting landscaping investment for homeowners and businesses alike.
 

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Artificial grass can become warm during peak summer heat, but modern turf products often come with cooling technologies or heat-reflective infills to reduce surface temperatures. You can also cool it down quickly with a light spray of water. Most homeowners find it still comfortable enough for pets and kids with some shading or planning.

 

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Yes! Most artificial grass products are non-toxic, lead-free, and soft underfoot, making them safe for children and pets. Many Las Vegas residents choose turf specifically designed for pet areas, which includes effective drainage systems and odor-reducing infill for cleanliness and hygiene.

 

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While artificial grass requires much less upkeep than natural grass, it still benefits from occasional maintenance. Light brushing, removing debris, and rinsing with water can keep your turf clean and looking fresh. For pet areas, routine deodorizing and proper drainage ensure a clean and odor-free space.

 

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Definitely. One of the biggest advantages of installing artificial grass in Las Vegas is the significant reduction in water usage. Since there's no need for irrigation, homeowners often see a noticeable drop in their water bills—plus it supports Las Vegas’ water conservation efforts amid ongoing drought conditions.

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