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首页> 外文期刊>Aquaculture >Relative importance of nitrogen and phosphorus emissions from shrimpfarming and other anthropogenic sources for six estuaries along the NEBrazilian coast
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Relative importance of nitrogen and phosphorus emissions from shrimpfarming and other anthropogenic sources for six estuaries along the NEBrazilian coast

机译:巴西内陆沿岸六个河口虾类养殖和其他人为来源的氮和磷排放量的相对重要性

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Shrimp aquaculture is a recent development of the Brazilian agribusiness but has increased by about 20% per year during the last decade along the semi-arid NE coast due to the optimal climate and environmental setting. The activity has been blamed to cause several environmental impacts mostly associated with the emission of large amounts of N and P to estuaries. Here we estimate, using an emission factor approach, the annual emissions of N and P from intensive shrimp farming and other anthropogenic sources and natural processes to six estuaries along the coast of Rio Grande do Norte State, NE Brazil, where about 40% of the shrimp farming area of the country is located. Emission factors for natural sources (atmospheric deposition and soil runoff) are 1 to 2 orders of magnitude lower than those from anthropogenic sources. Shrimp farming presents the largest average emission factors for N (1.9 t km super(-) super(2) yr super(-) super(1)), followed by agriculture (1.3 t km super(-) super(2) yr super(-) super(1)) and husbandry (0.7 t km super(-) super(2) yr super(-) super(1)). For P, largest average emission factors are from husbandry (0.9 t km super(-) super(2) yr super(-) super(1)) and agriculture (0.34 t km super(-) super(2) yr super(-) super(1)), although shrimp farming also presents a significant emission factor per unit of area for P (0.23 t km super(-) super(2) yr super(-) super(1)). Wastewaters and solid waste disposal and urban runoff present much lower emission factors per unit of area, due to the low level of urbanization and small population of the basins. Anthropogenic emissions of N and P are 20 to 50 times higher than natural emissions. Agriculture contributes with the larger fraction (40% to 63%) of the total annual N load to three of the rivers, whereas P emissions are dominated by husbandry (64% to 74%). Wastewaters contribute with significant loads of N and P to the more populated basin only (35% and 11%, for N and P, respectively). Urban runoff is practically negligible in all basins, (less than 5% of the total emission), with the exception of Guamare basin where 22% of the N emission come from this source. Aquaculture is the most important source of N to the Acu basin (58%), where the largest pond surface is observed. In the other basins N contribution from aquaculture ranges from 2% to 22%. Aquaculture contribution to the total P emission is small in all basins, varying from 2% to 14%. Notwithstanding the small area covered by shrimp farms relative to agriculture or husbandry, the location of farms adjacent to estuarine areas makes possible direct inputs to estuarine waters, while most other emissions go firstly to soils before eventually being transported to surface waters. In general, hydrochemical proxies of nutrient loads were consistent with the estimated loads.
机译:虾类水产养殖是巴西农业综合企业的最新发展,但由于最佳的气候和环境设置,在过去的十年中,沿半干旱的东北沿海地区,虾类养殖每年以约20%的速度增长。人们指责该活动造成了几种环境影响,这些影响主要与向河口排放大量的N和P有关。在这里,我们使用排放因子方法估算集约化虾类养殖及其他人为来源和自然过程向北巴西里奥格兰德州沿海地区的六个河口排放的氮和磷的年排放量,其中约40%该国位于虾类养殖区。自然来源(大气沉积和土壤径流)的排放因子比人为来源的排放因子低1-2个数量级。虾类养殖呈现最大的N平均排放因子(1.9 t km super(-)super(-)super(1)),其次是农业(1.3 t km super(-)super(2)yr super (-)super(1))和畜牧业(0.7 t km super(-)super(2)年super(-)super(1))。对于P,最大的平均排放因子来自畜牧业(0.9 t km超级(-)超级(-)超级(-)超级(1))和农业(0.34 t km超级(-)超级(2)yr超级(-) )super(1)),尽管虾类养殖也为P带来了每单位面积显着的排放因子(0.23 t km super(-)super(2)yr super(-)super(1))。由于城市化水平低和流域人口少,废水和固体废物处置以及城市径流的单位面积排放因子要低得多。 N和P的人为排放量是自然排放量的20至50倍。农业每年向三个河流贡献的氮量占总氮负荷的比例较大(40%至63%),而磷的排放量主要由畜牧业(64%至74%)控制。废水仅在人口稠密的盆地中贡献大量的N和P(分别为N和P的35%和11%)。在所有流域,城市径流几乎可以忽略不计(不到总排放量的5%),但瓜玛尔流域除外,该国的氮排放量中有22%来自此。水产养殖是Acu盆地中最重要的N来源(占58%),该地区的池塘面积最大。在其他流域,水产养殖对氮的贡献在2%至22%之间。在所有流域中,水产养殖对总磷排放的贡献很小,从2%到14%不等。尽管相对于农业或畜牧业,虾类养殖场覆盖的面积很小,但由于养殖场位于河口地区附近,因此有可能直接投入河口水,而大多数其他排放物首先进入土壤,最后被运输到地表水。通常,营养物负荷的水化学代理与估计负荷一致。

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