李洪枚
(首都經(jīng)濟(jì)貿(mào)易大學(xué) 安全與環(huán)境工程學(xué)院,北京 100070)
城市污水處理廠存在物理、化學(xué)、生物和人機(jī)工程及社會(huì)心理(ergonomic and psychosocial hazards)等幾種類型的職業(yè)健康危害因素[1]?;埂⒌?、中毒或感染(微生物)、皮膚病和聽力損傷是污水處理廠幾種常見的職業(yè)傷害,其中中毒或感染尤為受關(guān)注[2]。調(diào)查顯示:城市污水處理廠工人患癌癥和呼吸系統(tǒng)疾病的發(fā)病率明顯高于普通人群[3-5]。2015年美國(guó)勞工局職業(yè)傷害率統(tǒng)計(jì)顯示:污水處理廠職業(yè)傷害率為4.5%,高于美國(guó)平均職業(yè)傷害率3.0%[6]。因此,污水處理廠被視為危險(xiǎn)工作環(huán)境之一,其職業(yè)健康風(fēng)險(xiǎn)已成為國(guó)外職業(yè)健康領(lǐng)域的重要研究方向之一。
我國(guó)城鎮(zhèn)污水處理規(guī)模比較大,截止2015年6月,僅城鎮(zhèn)污水處理廠就已達(dá)到3802座[7],從業(yè)人數(shù)達(dá)到數(shù)十萬(wàn)。因此,有必要加強(qiáng)我國(guó)城市污水處理廠職業(yè)健康風(fēng)險(xiǎn)評(píng)估,為政府有關(guān)監(jiān)管部門和企業(yè)職業(yè)健康管理部門進(jìn)一步采取健康風(fēng)險(xiǎn)控制措施提供科學(xué)依據(jù)。本文就國(guó)內(nèi)外城市污水處理廠職業(yè)健康風(fēng)險(xiǎn)評(píng)估現(xiàn)狀進(jìn)行綜述和展望。
污水處理廠廠區(qū)一般可分為生產(chǎn)區(qū)和辦公區(qū)2個(gè)部分。生產(chǎn)區(qū)包括:格柵間、泵房、鼓風(fēng)機(jī)房、生化池(曝氣池、厭氧池和缺氧池等)、分配井、沉淀池、污泥濃縮池、消化罐、加藥室、消毒池(加氯間或臭氧發(fā)生器)、過(guò)濾池、污泥脫水車間和污泥運(yùn)輸?shù)榷鄠€(gè)工藝單元。辦公區(qū)包括:辦公樓、化驗(yàn)室和中控室等。污水處理工藝涉及的職業(yè)危害因素主要包括:噪聲、有毒有害物質(zhì)、病原微生物、夏季高溫輻射和高頻電場(chǎng)等,如表1所示。
表1 城市污水處理廠職業(yè)危害因素Table 1 Occupational hazards in urban sewage treatment plant
污水處理廠作業(yè)環(huán)境職業(yè)危害特點(diǎn)包括:
1)污水處理設(shè)備設(shè)施多是露天設(shè)置,自動(dòng)化程度較高,作業(yè)人員主要工作是巡檢、故障排除和維修。
2)辦公樓與污水處理設(shè)施距離較近,辦公人員會(huì)受到排放的有毒有害氣體影響。
3)職業(yè)危害因素種類不僅與污水處理工藝、設(shè)備設(shè)施和總圖布置有關(guān),還與污水來(lái)源和性質(zhì)有關(guān)。因此,不同城市污水處理廠職業(yè)危害因素的種類不同。
自本世紀(jì)初以來(lái),國(guó)內(nèi)有關(guān)職業(yè)衛(wèi)生研究與評(píng)價(jià)機(jī)構(gòu)依據(jù)職業(yè)衛(wèi)生標(biāo)準(zhǔn)或規(guī)范相繼開展了污水處理廠職業(yè)危害因素的現(xiàn)場(chǎng)調(diào)查識(shí)別、采樣檢測(cè)分析、危害分級(jí)和職業(yè)病危害控制效果評(píng)價(jià)等工作,對(duì)現(xiàn)場(chǎng)超過(guò)職業(yè)接觸限值的危害因素,提出相應(yīng)的對(duì)策措施[8-11]。如韓鈺等[8]采用現(xiàn)場(chǎng)檢測(cè)方法對(duì)某城市污水處理廠多個(gè)工藝單元的有毒有害氣體和噪聲等職業(yè)危害因素進(jìn)行檢測(cè)評(píng)估,結(jié)果發(fā)現(xiàn):曝氣控制室的噪聲和污泥脫水間的硫化氫測(cè)定值均超過(guò)職業(yè)接觸限值;劉俊玲[9]對(duì)某污水處理系統(tǒng)建設(shè)項(xiàng)目職業(yè)病危害控制效果進(jìn)行竣工驗(yàn)收評(píng)價(jià),結(jié)果表明:職業(yè)病危害因素均未超過(guò)職業(yè)接觸限值, 接觸危害因素的在崗職工職業(yè)健康檢查未發(fā)現(xiàn)職業(yè)病癥或職業(yè)禁忌癥。我國(guó)早期城市污水處理廠職業(yè)健康風(fēng)險(xiǎn)評(píng)估是職業(yè)暴露評(píng)估,并未涉及健康評(píng)估,主要針對(duì)噪聲、有毒有害氣體、高頻電場(chǎng)、夏季高溫和照度等職業(yè)危害因素[8-11],污水處理過(guò)程釋放的多種揮發(fā)性污染物和微生物氣溶膠的職業(yè)健康風(fēng)險(xiǎn)評(píng)估還很欠缺。
近年來(lái),國(guó)內(nèi)研究人員開始對(duì)我國(guó)城市污水處理廠工藝單元釋放的空氣污染物進(jìn)行定量分析,有關(guān)研究結(jié)果參見表2。由表2可以看出:污水處理過(guò)程釋放空氣污染物種類多,包括烷烴、烯烴、芳香烴、鹵代烴、含硫有機(jī)物、含氧有機(jī)物、H2S,CS2和NH3等幾十種揮發(fā)性污染物;揮發(fā)性污染物釋放強(qiáng)度不同,格柵、沉砂池和污泥處理等單元釋放量大, 惡臭濃度高[13-19],格柵和沉砂池惡臭濃度高是由于污水在城市管網(wǎng)中缺氧時(shí)間長(zhǎng),厭氧微生物分解廢水中有機(jī)物產(chǎn)生較多惡臭氣體,剛進(jìn)入污水處理設(shè)施釋放量大,而污泥處理過(guò)程存在厭氧環(huán)境造成厭氧微生物分解污泥產(chǎn)生多種惡臭氣體;不同污水處理工藝、氣候和反應(yīng)條件等因素會(huì)影響揮發(fā)性污染物的釋放速率和釋放強(qiáng)度[16-17],文獻(xiàn) [16]是開發(fā)區(qū)污水處理廠,工業(yè)污水較多,處理過(guò)程釋放的揮發(fā)性污染物濃度高;H2S是惡臭主要成分[17-19,21],最高濃度達(dá)到145.7 mg/m3,H2S釋放與氣候和反應(yīng)條件等因素之間存在相關(guān)性,但其他揮發(fā)性污染物釋放特征與工藝條件等因素的相關(guān)性研究還很缺乏。
表2 我國(guó)城市污水處理廠空氣污染物釋放特征*Table 2 Emission characteristics of air pollutants from wastewater treatment plants in China
*表中各文獻(xiàn)報(bào)道的空氣采樣點(diǎn)是從污水進(jìn)水渠、格柵、沉砂池、初沉池、生化池(曝氣、缺氧、厭氧等)、二沉池、污泥濃縮池、污泥脫水、污泥儲(chǔ)存和辦公樓等作業(yè)場(chǎng)所或工作場(chǎng)所選取部分單元作為采樣檢測(cè)點(diǎn),具體采樣點(diǎn)可參考原文獻(xiàn)。
基于污水處理廠空氣污染物釋放特征研究,研究人員開始對(duì)污水處理廠空氣污染物職業(yè)健康風(fēng)險(xiǎn)進(jìn)行評(píng)估,有關(guān)研究結(jié)果參見表3。由表3可以看出:評(píng)估方法主要采用美國(guó)環(huán)保署推薦的健康風(fēng)險(xiǎn)評(píng)價(jià)模型進(jìn)行評(píng)估,因致癌斜率因子和非致癌參考劑量數(shù)據(jù)缺乏,目前,僅對(duì)部分苯系物和鹵代烴等幾種揮發(fā)性污染物的職業(yè)健康風(fēng)險(xiǎn)進(jìn)行了評(píng)估[18-20, 24],VOS、鹵代芳香烴、鹵代酸酯和含氧有機(jī)物等[12-13]多種有毒有害氣體的職業(yè)健康風(fēng)險(xiǎn)評(píng)估有待進(jìn)一步開展; 我國(guó)城市污水廠微生物氣溶膠職業(yè)健康風(fēng)險(xiǎn)評(píng)估研究處于起步階段,相關(guān)研究報(bào)道很少[22],微生物氣溶膠中微生物種群分布特征、各種微生物與人類健康之間的劑量—效應(yīng)關(guān)系和微生物氣溶膠暴露因子等基礎(chǔ)研究工作還非常缺乏,有待進(jìn)一步開展。
表3 我國(guó)城市污水處理廠職業(yè)健康風(fēng)險(xiǎn)評(píng)估Table 3 Occupational health risk assessment in wastewater treatment plants in China
*終身致癌風(fēng)險(xiǎn)(LCR):LCR=CDI×SF, 式中LCR:終身致癌風(fēng)險(xiǎn);CDI:污染物暴露量(mg/kg·d);SF:致癌斜率因子(kg/mg·d)。LCR<10-6時(shí),可以接受;10-6
國(guó)外主要采用GC-MS、臭覺(jué)法、電子鼻和微生物采樣培養(yǎng)等方法對(duì)城市污水處理廠工藝單元釋放的空氣污染物進(jìn)行檢測(cè)和表征,為職業(yè)健康風(fēng)險(xiǎn)評(píng)估提供依據(jù)[25],有關(guān)研究結(jié)果參見表4。
表4 國(guó)外城市污水處理廠空氣污染物釋放特征*Table 4 Emission characteristics of air pollutants from wastewater treatment plants abroad
續(xù)表4
*表中各文獻(xiàn)報(bào)道的空氣采樣點(diǎn)是從污水進(jìn)水渠、格柵、沉砂池、初沉池、生化池、二沉池、污泥濃縮池、污泥儲(chǔ)存、污泥脫水、污水分流建構(gòu)筑物和辦公樓等作業(yè)場(chǎng)所或工作場(chǎng)所選取部分單元作為采樣檢測(cè)點(diǎn),具體采樣點(diǎn)可參考原文獻(xiàn)。
由表4可以看出:污水處理單元釋放的揮發(fā)性污染物包括H2S,VOS、苯系物、有機(jī)小分子酸、醛、酮和胺等數(shù)十種[26-27,29],其中H2S濃度高達(dá)14 mg/m3 [27]或95×10-6[30];污水預(yù)處理單元(進(jìn)水渠、格柵間和初沉池)和污泥處理單元(濃縮、脫水和熱干化)臭味濃度和釋放速率高[31-36],但不同工藝單元臭氣釋放強(qiáng)度和速率差別比較大,文獻(xiàn)[32]和[34]報(bào)道的結(jié)果比較低,臭味濃度在12~800 OU/m3之間;而文獻(xiàn)[36]報(bào)道的結(jié)果很高,最高達(dá)到19 916 OU/m3,可能與污水處理技術(shù)和管理水平有關(guān)。另外臭味濃度與VOCs之間呈良好的線性關(guān)系[31];污水處理單元釋放到空氣中的生物氣溶膠含內(nèi)毒素、細(xì)菌、放線菌、真菌和病毒等多種微生物群[37-38],曝氣池周圍空氣中細(xì)菌濃度夏天最大[39],這由于曝氣使含微生物水滴容易在空氣中形成更多的氣溶膠顆粒。
不難看出,國(guó)內(nèi)外城市污水處理廠工藝單元釋放的空氣污染物種類基本一致,即揮發(fā)性污染物和生物氣溶膠,但國(guó)內(nèi)在生物氣溶膠暴露研究方面還比較欠缺。鑒于化學(xué)分析成本高,國(guó)外目前主要采用臭覺(jué)測(cè)量法(基本上都采用歐盟的EN 13725:2003)[30,32-36]和微生物空氣采樣培養(yǎng)法量化城市污水處理廠空氣污染物的釋放特征[37-39]。
國(guó)外城市污水處理廠職業(yè)健康風(fēng)險(xiǎn)評(píng)估始于上世紀(jì)八十年代[40],有關(guān)研究參見表5。
國(guó)外城市污水處理廠職業(yè)健康風(fēng)險(xiǎn)評(píng)估主要采取問(wèn)卷調(diào)查及生理指標(biāo)測(cè)量[41,48]、矩陣法[44]、生物標(biāo)記法[42-43]和劑量-反應(yīng)模型[45-47]。由文獻(xiàn)[41]和[48]研究結(jié)果可知,污水處理廠工藝單元釋放的臭氣和生物氣溶膠與工人的生理(呼吸系統(tǒng)病狀)和心理健康(厭惡感、消沉等心理問(wèn)題)存在一定的相關(guān)性。矩陣法確定各種職業(yè)危害因素的健康風(fēng)險(xiǎn),方法簡(jiǎn)單,但主觀性較強(qiáng)[44]。劑量-反應(yīng)模型評(píng)估結(jié)果顯示,污水入口處和污泥處理單元感染病毒的概率比較大[45-47],但氣溶膠中各種微生物職業(yè)暴露感染機(jī)理不明確,難以確定生物氣溶膠暴露與工人的實(shí)際病狀或發(fā)病率之間的相關(guān)性。生物標(biāo)記法直接采集暴露者的生物樣本,評(píng)估多環(huán)芳烴和苯暴露的基因損傷和致癌風(fēng)險(xiǎn)[42-43],結(jié)果表明室外工人職業(yè)暴露致癌風(fēng)險(xiǎn)明顯高于室內(nèi)辦公人員,這也為污水處理廠工人癌癥發(fā)病率高的現(xiàn)象提供了可能的解釋[49-50]。
表5 國(guó)外城市污水處理廠職業(yè)健康風(fēng)險(xiǎn)評(píng)估Table 5 Occupational health risk assessment in wastewater treatment plants abroad
我國(guó)城市污水處理廠職業(yè)健康風(fēng)險(xiǎn)評(píng)估工作主要有:依據(jù)有關(guān)職業(yè)接觸限值,對(duì)噪聲和有毒有害氣體等常規(guī)職業(yè)健康危害因素進(jìn)行調(diào)查、檢測(cè)和暴露評(píng)估;用化學(xué)法對(duì)污水處理單元釋放的多種揮發(fā)性污染物進(jìn)行檢測(cè)和表征;對(duì)部分揮發(fā)性有機(jī)物和微生物進(jìn)行職業(yè)健康風(fēng)險(xiǎn)評(píng)估。評(píng)估方法從合規(guī)性暴露評(píng)價(jià)向綜合性健康風(fēng)險(xiǎn)評(píng)估發(fā)展,為進(jìn)一步優(yōu)化污水處理工藝,合理選擇臭氣治理技術(shù)[51],提高職業(yè)健康管理水平提供了科學(xué)依據(jù)。但揮發(fā)性污染物的釋放機(jī)理、釋放動(dòng)力學(xué)和預(yù)測(cè)模型等基礎(chǔ)研究還比較欠缺,VOS、鹵代芳香烴、鹵代酸酯和含氧有機(jī)物等有毒有害氣體[12-13],以及生物氣溶膠的職業(yè)健康風(fēng)險(xiǎn)評(píng)估等研究有待進(jìn)一步開展。
國(guó)外城市污水處理廠職業(yè)健康風(fēng)險(xiǎn)評(píng)估已形成比較系統(tǒng)的職業(yè)暴露檢測(cè)和健康風(fēng)險(xiǎn)評(píng)估方法。暴露檢測(cè)方法有:化學(xué)法、臭覺(jué)法、電子鼻[27]、微生物采樣培養(yǎng)、生物標(biāo)記[41]、化學(xué)傳感器[52]和模型預(yù)測(cè)法[32,53-54];健康風(fēng)險(xiǎn)評(píng)估方法有:?jiǎn)柧碚{(diào)查及生理檢測(cè)、矩陣法、生物標(biāo)記法和劑量-反應(yīng)模型等[41-48]。但臭氣中多種揮發(fā)性污染物復(fù)合毒性和生物氣溶膠中各種微生物的職業(yè)暴露致病機(jī)理還不明確,難以確定職業(yè)暴露發(fā)病癥狀與暴露之間的關(guān)系。
綜上,城市污水處理廠職業(yè)健康風(fēng)險(xiǎn)評(píng)估在以下幾個(gè)方面還有待深入研究:
1)職業(yè)危害因素種類問(wèn)題。目前的研究主要針對(duì)揮發(fā)性污染物和生物氣溶膠職業(yè)健康風(fēng)險(xiǎn),而噪聲、人機(jī)工程和社會(huì)心理等職業(yè)危害因素的健康風(fēng)險(xiǎn)評(píng)估還很缺乏。
2)暴露特征污染物問(wèn)題。污水處理釋放的揮發(fā)性污染物和微生物種類都很多,如何根據(jù)各種揮發(fā)性污染物或微生物暴露水平及其健康風(fēng)險(xiǎn)的大小,確定特征污染物,以減少監(jiān)測(cè)量,同時(shí)加強(qiáng)各種污染物釋放機(jī)理和動(dòng)力學(xué)研究,建立可靠的預(yù)測(cè)模型。
3)暴露水平與實(shí)際病狀或發(fā)病率關(guān)系問(wèn)題。雖然揮發(fā)性污染物和生物氣溶膠的暴露與污水處理廠工人的有關(guān)病狀或發(fā)病率存在一定的相關(guān)性,但不能明確是哪些或哪幾種污染物對(duì)工人健康造成傷害,需深入研究暴露致病過(guò)程或機(jī)理。
4)復(fù)合污染物健康風(fēng)險(xiǎn)問(wèn)題。污水處理廠工作場(chǎng)所大部分是室外露天環(huán)境,不僅有工藝過(guò)程釋放的多種揮發(fā)性污染物和生物氣溶膠,而且還有大氣污染物(如PM2.5和PM10),形成了固體顆粒物、多種揮發(fā)性污染物和生物氣溶膠等組成的復(fù)合污染物,有必要研究復(fù)合污染物健康風(fēng)險(xiǎn)評(píng)價(jià)模型或方法[55]。
5)職業(yè)危害因素與非職業(yè)危害因素問(wèn)題。污水處理廠工人的健康不僅受到工作場(chǎng)所的物理、化學(xué)、生物和人機(jī)工程等職業(yè)危害因素的影響,而且還受到非職業(yè)環(huán)境因素影響(如家庭問(wèn)題)。職業(yè)與非職業(yè)危害因素的復(fù)合對(duì)工人健康影響,有待研究[56]。
[1]International Labour Organization. Operator, Wastewater treatment plant: International Hazard Datasheets on Occupation[EB/OL]. (2012-07-04)[2016-11-29]. http://www.ilo.org/safework/cis/WCMS_192394/lang--en/index.htm.
[2]Heinonen-Tanski H, Reponen T, Koivunen J. Airborne enteric coliphages and bacteria in sewage treatment plants[J]. Water Research, 2009, 43(9):2558-66.
[3]Lidwien A M Smit, Suzanne Spaan, Dick J J Heederik. Endotoxin exposure and symptoms in wastewater treatment workers[J]. American Journal of Industrial Medicine, 2005,48(1):30-39.
[4]LAFLEUR J, VENA J E. Retrospective cohort mortality study of cancer among sewage plant workers[J]. American Journal of Industrial Medicine, 1991, 19(1): 75-86.
[5]Olin R G, Ahlbom A, Lindberg-Navier I, et al. Occupational factors associated with astrocytomas: a case-control study. American Journal of Industrial Medicine, 1987, 11:615-625.
[6]U.S. Department of Labor. EMPLOYER-REPORTED WORKPLACE INJURIES AND ILLNESSES-2015 [EB/OL]. (2016-10-27) [2016-11-29]. http://www.bls.gov/news.release/pdf/osh.pdf.
[7]中華人民共和國(guó)住房和城鄉(xiāng)建設(shè)部. 住房城鄉(xiāng)建設(shè)部關(guān)于全國(guó)城鎮(zhèn)污水處理設(shè)施2015年第二季度建設(shè)和運(yùn)行情況的通報(bào)(建城函[2015]205號(hào))[EB/OL]. (2015-07-27) [2016-11-29]. http://www.mohurd.gov.cn/wjfb/201508/t20150817_223298.html.
[8]韓鈺,王晶.北方某污水處理廠職業(yè)病危害因素檢測(cè)結(jié)果分析[J].職業(yè)與健康,2006,22(11):822-823.
HAN Yu, WANG Jing. Analysis on the results of occupational disease risk factors detected in a sewage treatment plant in north China[J]. Occupation and Health, 2006,22(11): 822-823.
[9]劉俊玲. 某生活污水處理系統(tǒng)職業(yè)病危害控制效果評(píng)價(jià)[J].中國(guó)衛(wèi)生工程學(xué),2015,14(3):265-269.
LIU Junling. Evaluation on control effect of occupational hazards in a sewage treatment system[J]. China J of Public Health Eng, 2015,14 (3):265-269.
[10]王曉軻,張曉杰,楊冠榮,等. 漯河市某縣污水處理廠職業(yè)病危害控制效果評(píng)價(jià)[J]. 中國(guó)城鄉(xiāng)企業(yè)衛(wèi)生,2013(6):100-101.
WANG Xiaoke, ZHANG Xiaojie, YANG Guanrong, et al. Evaluation on the effect of occupation disease hazard control in a sewage treatment plant in Luohe City[J]. Chinese Journal of Urban and Rural Enterprise Hygiene, 2013(6):100-101.
[11]曾東,耿琪,楊金龍. 城市污水處理的職業(yè)病危害分析與防護(hù)對(duì)策[J]. 中國(guó)衛(wèi)生工程學(xué),2014, 13(1):5-7.
ZENG Dong, GENG Qi, YANG Jinlong. Analysis and prevention of occupational hazards in urban sewage treatment[J]. China J of Public Health Eng, 2014, 13(1):5-7.
[12]唐小東. 城市污水處理廠揮發(fā)性有機(jī)惡臭污染物的來(lái)源及感官定量評(píng)價(jià)[D]. 廣州:暨南大學(xué),2011.
[13]馮志誠(chéng). 城市典型惡臭源的揮發(fā)性有機(jī)物的分子標(biāo)志物初步研究[D]. 廣州:暨南大學(xué),2009.
[14]劉舒樂(lè),王伯光,何潔,等. 城市污水處理廠惡臭揮發(fā)性有機(jī)物的感官定量評(píng)價(jià)研究[J]. 環(huán)境科學(xué), 2011, 32 (12 ) :3582-3587.
LIU Shule,WANG Boguang,HE Jie,et al. Quantification assessment of the relationship between chemical and olfactory concentrations for malodorous volatile organic compounds[J]. Environmental Science, 2011, 32 (12 ) :3582-3587.
[15]何潔,王伯光,劉舒樂(lè),等. 城市污水處理廠揮發(fā)性鹵代有機(jī)物的排放特征及影響因素研究[J]. 環(huán)境科學(xué),2011,32(12):3577- 3581.
HE Jie,WANG Boguang,LIU Shule,et al. Source emission characteristics and impact factors of volatile halogenated organic compounds from wastewater treatment plant[J]. Environmental Science, 2011,32(12):3577- 3581.
[16]盛彥清. 廣州市典型污染河道與城市污水處理廠中惡臭有機(jī)硫化物的初步研究[D]. 廣州:中國(guó)科學(xué)院研究生院(廣州地球化學(xué)研究所), 2007.
[17]王智超.城市污水處理廠硫化氫排放特征及釋放模型研究[D]. 北京:清華大學(xué), 2013.
[18]高爽. 惡臭污染源揮發(fā)性有機(jī)物排放特征和健康風(fēng)險(xiǎn)評(píng)估[D]. 天津:南開大學(xué),2012.
[19]王秀艷,易忠芹,王釗,等. 污水處理廠惡臭氣體健康風(fēng)險(xiǎn)評(píng)估[J]. 土木建筑與環(huán)境工程,2013,35(5):50-54.
WANG Xiuyan, YI Zhongqin, WANG Zhao, et al. Health risk assessment of odor gases from sewage treatment plant. Journal of Civil Architectural & Environmental Engineering, 2013,35(5):50-54.
[20]YANG Junchen, WANG Kun, ZHAO Qingliang, et al. Underestimated public health risks caused by overestimated VOC removal in wastewater treatment processes[J]. Environmental Science. Processes & Impacts, 2014, 16(2): 271-279.
[21]ZHANG Chun-hui, WANG Liang-liang, WANG Xiao-chan, et al. Odor emission impact assessment of Zhengwangfen wastewater treatment plant in Beijing[J]. Desalination and Water Treatment, 2016, 57(38): 17901-17910.
[22]邱雄輝. 污水廠微生物氣溶膠的逸散特征、傳輸特征及健康風(fēng)險(xiǎn)研究[D]. 西安:長(zhǎng)安大學(xué),2012.
[23]LI Jing, ZHOU Lian-tong, ZHANG Xiang-yu, et al. Bioaerosol emissions and detection of airborne antibiotic resistance genes from a wastewater treatment plant[J]. Atmospheric Environment, 2016, 124(B): 404-412.
[24]YANG Wen-ben, CHEN W H, YUAN C S, et al. Comparative assessments of VOC emission rates and associated health risks from wastewater treatment processes[J]. Journal of Environmental Monitoring : JEM, 2012, 14(9): 2464-2474.
[25]ELIA V J, CLARK C S, MAJETI V A, et al. Hazardous chemical exposure at a municipal wastewater treatment plant[J]. Environmental Research, 1983, 32(2): 360-371.
[26]LASARIDI K, KATSABANIS G, KYRIACOU A, et al. Assessing odour nuisance from wastewater treatment and composting facilities in Greece[J]. Waste Management & Research : the Journal of the International Solid Wastes and Public Cleansing Association, ISWA, 2010, 28(11): 977-984.
[27]LEHTINEN J, VEIJANEN A. Determination of odorous VOCs and the risk of occupational exposure to airborne compounds at the waste water treatment plants[J]. Water Science and Technology : a Journal of the International Association on Water Pollution Research, 2011, 63(10): 2183-2192.
[28]CHENG Xianhao, PETERKIN E, BURLINGAME G A. A study on volatile organic sulfide causes of odors at Philadelphia's Northeast Water Pollution Control Plant[J]. Water Research, 2005, 39(16): 3781-3790.
[29]Zarra T, Reiser M, Naddeo V, et al. Odour emissions characterization from wastewater treatment plants by different measurement methods[J]. Chemical Engineering Transactions, 2014, 40:37-42.
[30]C. David Cooper P.E. QEP, Victor J G P E, Ray H P E, et al. Odor investigation and control at a WWTP in orange county, florida[J]. Environmental Progress & Sustainable Energy, 2001, 20(3):133-143.
[31]DINCER F, MUEZZINOGLU A. Odor-causing volatile organic compounds in wastewater treatment plant units and sludge management areas[J]. Journal of Environmental Science and Health. Part a, Toxic/Hazardous Substances & Environmental Engineering, 2008, 43(13): 1569-1574.
[32]Frechen F B.Odour emission and odour control at wastewater treatment plants in West Germany[J].Water Sci and Technol,1988,20(4-5):261-266.
[33]Philip Wolstenholme. Odor control at wastewater treatment plants: A significant shift in odor objectives[J]. Florida Water Resources Journal, 2013(6):16-23.
[34]Vincenzo Naddeo, Tiziano Zarra, Stefano Giuliani, et al. Odour Impact Assessment in Industrial Areas[J]. Chemical Engineering Transactions, 2012, 30: 85 -90.
[35]Zarra T, Giuliani S, Naddeo V, et al. Odour impact evaluation from wastewater treatment plant[A]// International Conference on Environmental Science & Technology[C]. 2011:2065-2072.
[37]LAITINEN S, KANGAS J, KOTIMAA M, et al. Workers' exposure to airborne bacteria and endotoxins at industrial wastewater treatment plants[J]. American Industrial Hygiene Association Journal, 1994, 55(11): 1055-1060.
[38]KORZENIEWSKA E, FILIPKOWSKA Z, GOTKOWSKA-PACHTA A, et al. Determination of emitted airborne microorganisms from a BIO-PAK wastewater treatment plant[J]. Water Research, 2009, 43(11): 2841-2851.
[39]NIAZI S, HASSANVAND M S, MAHVI A H, et al. Assessment of bioaerosol contamination (bacteria and fungi) in the largest urban wastewater treatment plant in the Middle East[J]. Environmental Science and Pollution Research International, 2015, 22(20): 16014-16021.
[40]SCARLETT-KRANZ J M, BABISH J G, STRICKLAND D, et al. Urinary mutagens in municipal sewage workers and water treatment workers[J]. American Journal of Epidemiology, 1986, 124(6): 884-893.
[41]Abdou M H. Health impacts on workers in wastewater treatment plants in jeddah city, saudi arabia.[J]. Journal of the Egyptian Public Health Association, 2007, 82(5-6):405-417.
[42]Al Z H, Ferrari L, Laurent A M, et al. Biomonitoring of complex occupational exposures to carcinogens: the case of sewage workers in Paris[J]. BMC Cancer, 2008, 8(1):1-10.
[43]Zabadi H A, Ferrari L, Sariminodier I, et al. Integrated exposure assessment of sewage workers to genotoxicants: an urinary biomarker approach and oxidative stress evaluation[J]. Environmental Health, 2011, 10(1):1-14.
[44]Malakahmad A, Downe A G, Fadzil S D M. Application of occupational health and safety management system at sewage treatment plants[A]// Business Engineering and Industrial Applications Colloquium[C]. IEEE, 2012:347-350.
[45]Medema G, Wullings B, Roeleveld P, et al. Risk assessment of Legionella and enteric pathogens in sewage treatment works[J]. Water Science & Technology Water Supply, 2004, 4(2):125-132.
[46]WESTRELL T, SCH?NNING C, STENSTR?M T A, et al. QMRA (quantitative microbial risk assessment) and HACCP (hazard analysis and critical control points) for management of pathogens in wastewater and sewage sludge treatment and reuse[J]. Water Science and Technology : a Journal of the International Association on Water Pollution Research, 2004, 50(2): 23-30.
[47]CARDUCCI A, DONZELLI G, CIONI L, et al. Quantitative microbial risk assessment in occupational settings applied to the airborne human adenovirus infection[J]. International Journal of Environmental Research and Public Health, 2016, 13(7): 733-743.
[48]Jahangiri M, Neghab M, Nasiri G, et al. Respiratory disorders associated with in wastewater treatment plants[J]. Journal of Occupational and Environmental Medicine,2015,6(1):41-49.
[49]WILD P, AMBROISE D, BENBRIK E, et al. Mortality among Paris sewage workers[J]. Occupational and Environmental Medicine, 2006, 63(3): 168-172.
[50]FRIIS L, MIKOCZY Z, HAGMAR L, et al. Cancer incidence in a cohort of Swedish sewage workers: extended follow up[J]. Occupational and Environmental Medicine, 1999, 56(10): 672-673.
[51]Chen W H, Yang W B, Yuan C S, et al. Fates of chlorinated volatile organic compounds in aerobic biological treatment processes: the effects of aeration and sludge addition.[J]. Chemosphere, 2014, 103(5):92-98.
[52]ZIYA OZTüRK Z, TASALTIN C, ENGIN G O, et al. Evaluation of a fast wastewater odour characterisation procedure using a chemical sensor array[J]. Environmental Monitoring and Assessment, 2009, 151(1/4): 369-375.
[53]Llavador C F, Espinós M H, Mantilla I E. Estimation of hydrogen sulfide emission rates at several wastewater treatment plants through experimental concentration measurements and dispersion modeling[J]. Journal of the Air & Waste Management Association, 2012, 62(7):758.
[54]Schauberger G, Piringer M, Baumannstanzer K, et al. Use of a Monte Carlo technique to complete a fragmented set of H2S emission rates from a wastewater treatment plant[J]. Journal of Hazardous Materials,2013,263: 694-701.
[55]王凡.典型室內(nèi)空氣復(fù)合污染物對(duì)多靶器官毒性評(píng)價(jià)研究[D].大連:大連理工大學(xué),2013.
[56]LENTZ T J, DOTSON G S, WILLIAMS P R, et al. Aggregate exposure and cumulative risk Assessment--Integrating occupational and non-occupational risk factors[J]. Journal of Occupational and Environmental Hygiene, 2015, 12(S1): S112-S126.
中國(guó)安全生產(chǎn)科學(xué)技術(shù)2017年6期