| 5 | 1/1 | 返回列表 |
| 查看: 725 | 回復(fù): 2 | |||
| 本帖產(chǎn)生 1 個(gè) 翻譯EPI ,點(diǎn)擊這里進(jìn)行查看 | |||
| 當(dāng)前只顯示滿(mǎn)足指定條件的回帖,點(diǎn)擊這里查看本話(huà)題的所有回帖 | |||
jsyhn木蟲(chóng) (小有名氣)
|
[交流]
懸賞翻譯一篇400多字的摘要(環(huán)境,納米,土壤相關(guān))
|
||
|
請(qǐng)高手在今天0點(diǎn)以前幫忙翻譯好,100金幣就歸您了!非常感謝,萬(wàn)分感謝! 內(nèi)容為: 通過(guò)比較納米氧化銅 (CuO NPs), 微米氧化銅 (CuO MPs)在兩種土壤中的Cu2+溶出及其對(duì)脲酶活性影響, 結(jié)合可產(chǎn)生脲酶活性抑制效應(yīng)的Cu2+濃度閾值, 研究了CuO NPs和CuO MPs對(duì)土壤脲酶活性的毒性效應(yīng)機(jī)制. 結(jié)果表明: CuO NPs和CuO MPs的Cu2+溶出量隨其濃度增加而增加, 溶出比率隨濃度增加而減少, 兩者在紅壤中的Cu2+溶出均高于其在烏柵土中;在1~100 mg • kg-1范圍內(nèi), CuO NPs對(duì)土壤脲酶活性產(chǎn)生了顯著(p ≤0.05)或極顯著(p ≤0.01)的抑制效應(yīng), 同濃度下, CuO NPs在土壤中的Cu2+溶出及其對(duì)脲酶活性的抑制效應(yīng)均大于CuO MPs; 在相對(duì)低濃度 (1~10 mg • kg-1, 紅壤; 1~100 mg • kg-1, 烏柵土)下, 納米顆粒態(tài)導(dǎo)致了CuO NPs對(duì)土壤脲酶活性的抑制毒性, 在相對(duì)高濃度 (≥50 mg • kg-1, 紅壤; ≥500 mg • kg-1, 烏柵土)下, 納米顆粒態(tài)和溶出Cu2+共同作用引起了脲酶活性抑制;與CuO NPs 不同, CuO MPs只有通過(guò)溶出Cu2+抑制土壤脲酶活性, 其顆粒態(tài)對(duì)脲酶活性無(wú)顯著影響; 值得注意的是, 在低濃度(1 mg • kg-1)下CuO NPs對(duì)土壤脲酶活性具有微米態(tài)和離子態(tài)所沒(méi)有的抑制毒性, 說(shuō)明其對(duì)土壤酶影響應(yīng)存在特殊機(jī)理, 值得進(jìn)一步深入研究. 輔助您翻譯的專(zhuān)業(yè)詞匯如下: 脲酶:urease 活性:activity 溶出:release 抑制:inhibit/inhibition 紅壤:Udic Ferrosols 烏柵土:Anthrosol |
至尊木蟲(chóng) (職業(yè)作家)
院士
| By comparing the nano-copper oxide (CuO NPs), micron copper oxide (CuO MPs) in two soil Cu2 + dissolution and its urease activity, combined to produce urease activity inhibition effect of the Cu2 + concentration threshold of the CuO NPs and CuO MPs on soil urease activity of the toxic effect mechanism. The results show that: CuO NPs and CuO MPs of Cu2 + dissolution increased with its concentration increases, dissolution rate with the concentration decreased, both in the red in the Cu2 + dissolution was higher than its In Wushan soil; in 1 ~ 100 mg • kg-1 range, CuO NPs on soil urease activity produced a significant (p ≤ 0.05) or highly significant (p ≤ 0.01) inhibitory effect, the same concentration, CuO NPs Cu2 + in the soil dissolution and on the inhibitory effect of urease activity was higher than CuO MPs; in relatively low concentrations (1 ~ 10 mg • kg-1, red; 1 ~ 100 mg • kg-1, Wushan soil) under nano-particle states leads to CuO NPs on urease activity inhibition of toxicity, a relatively high concentration (≥ 50 mg • kg-1, red; ≥ 500 mg • kg-1, Wushan soil), the nano-particulate and dissolved Cu2 + interaction caused urease activity inhibition; and CuO NPs different, CuO MPs only through the dissolution of Cu2 + inhibition of urease activity, the particulate on urease activity had no significant effect; It is noteworthy that, in low concentration (1 mg • kg-1 ) under the CuO NPs on soil urease activity states and ionic states with micron not inhibited by the toxicity, indicating its impact on soil enzyme should exist a special mechanism, it is worth further study. |

木蟲(chóng) (正式寫(xiě)手)
|
By comparing the Cu2+ release and the effects of urease's activity of CuO NPs and CuO MPs in two kinds of soil,combining the threshold concentration of Cu2+ which can have inhibiting action to urease's activity,we studied the mechanism of the toxic effects to soil urease's activity given by CuO NPs and CuO MPs.It showed that the Cu2+ release of CuO NPs and CuO MPs enhanced by the increasng of their concentrations, the dissolving rate was to the contrary.Both of their Cu2+ release are higher in Udic Ferrosols than Anthrosol .In the range of 1 to 100 mg • kg-1,CuO NPs had a prominent inhibiting action to urease with p ≤0.05 and highly significant action with p ≤0.01.In the same concentration,the Cu2+ release and the effects of urease's activity of CuO NPs was over to CuO MPs.In the relatively low concentration(1~10 mg • kg-1 in Udic Ferrosols and Anthrosol),the nanoparticle form resulted the inhibitorytoxicity of CuO NPs to urease's activity.In the relatively high concentration((≥50 mg • kg-1 in Udic Ferrosols,≥500 mg • kg-1 in Anthrosol),the synergy of nanoparticle form and Cu2+ release produced inhibiting action to urease's activity.Differing to CuO NPs,CuO MPs inhibited the activity of urease only through Cu2+ release,its nanoparticle form didn't have a remarkable influence.It's wroth to learn,CuO NPs had a inhibitorytoxicity in the low concentration(1 mg • kg-1) which the submicronin form and ionic form didn't have. That showed that there was a special mechanism for the influence of CuO NPs to soil enzyme taht's wroth to do a deep study.不知道能不能幫到你 |

| 最具人氣熱帖推薦 [查看全部] | 作者 | 回/看 | 最后發(fā)表 | |
|---|---|---|---|---|
|
[考研] 375求調(diào)劑 +4 | 雨夏整夜 2026-03-29 | 4/200 |
|
|---|---|---|---|---|
|
[考研] 南京大學(xué)化學(xué)調(diào)劑 +4 | 景隨風(fēng) 2026-03-29 | 7/350 |
|
|
[考研] 材料學(xué)碩333求調(diào)劑 +11 | 北道巷 2026-03-24 | 11/550 |
|
|
[考研] 0856求調(diào)劑 +7 | 楒桉 2026-03-28 | 7/350 |
|
|
[考研] 調(diào)劑考研 +3 | 王杰一 2026-03-29 | 3/150 |
|
|
[考研] 本科新能源科學(xué)與工程,一志愿華理能動(dòng)285求調(diào)劑 +7 | AZMK 2026-03-28 | 11/550 |
|
|
[考研] 283求調(diào)劑 +3 | A child 2026-03-28 | 3/150 |
|
|
[考研] 085600,材料與化工321分求調(diào)劑 +9 | 大饞小子 2026-03-28 | 9/450 |
|
|
[考研] 085701環(huán)境工程,267求調(diào)劑 +16 | minht 2026-03-26 | 16/800 |
|
|
[考研] 085405 考的11408求各位老師帶走 +3 | Qiu學(xué)ing 2026-03-28 | 3/150 |
|
|
[考研] 086502化學(xué)工程342求調(diào)劑 +6 | 阿姨復(fù)古不過(guò) 2026-03-27 | 6/300 |
|
|
[考研] 315分求調(diào)劑 +7 | 26考研上岸版26 2026-03-26 | 7/350 |
|
|
[考研] 291求調(diào)劑 +7 | 孅華 2026-03-22 | 7/350 |
|
|
[考研] 283求調(diào)劑(080500) +4 | A child 2026-03-27 | 4/200 |
|
|
[考研] 一志愿華東理工大學(xué)081700,初試分?jǐn)?shù)271 +6 | kotoko_ik 2026-03-23 | 7/350 |
|
|
[考研] 求調(diào)劑 +3 | 劉柯@ 2026-03-24 | 4/200 |
|
|
[考研] 324求調(diào)劑 +8 | hanamiko 2026-03-26 | 10/500 |
|
|
[考研] 化學(xué)工程085602 305分求調(diào)劑 +17 | RichLi_ 2026-03-25 | 17/850 |
|
|
[考研] 總分293求調(diào)劑 +6 | 加一一九 2026-03-25 | 8/400 |
|
|
[論文投稿] 急發(fā)核心期刊論文 +3 | 賢達(dá)問(wèn)津 2026-03-23 | 5/250 |
|